CN109544045A - A kind of beside street in city greenery patches vegetation spatial configuration method for supporting function based on bio-diversity - Google Patents
A kind of beside street in city greenery patches vegetation spatial configuration method for supporting function based on bio-diversity Download PDFInfo
- Publication number
- CN109544045A CN109544045A CN201811637697.8A CN201811637697A CN109544045A CN 109544045 A CN109544045 A CN 109544045A CN 201811637697 A CN201811637697 A CN 201811637697A CN 109544045 A CN109544045 A CN 109544045A
- Authority
- CN
- China
- Prior art keywords
- area
- street
- arbor
- greenery patches
- beside street
- 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.)
- Granted
Links
- 238000000034 method Methods 0.000 title claims abstract description 27
- 238000012856 packing Methods 0.000 claims description 2
- 241000271566 Aves Species 0.000 description 30
- 230000006870 function Effects 0.000 description 20
- 241000894007 species Species 0.000 description 18
- 230000000694 effects Effects 0.000 description 17
- 241000196324 Embryophyta Species 0.000 description 11
- 238000010586 diagram Methods 0.000 description 10
- 238000011835 investigation Methods 0.000 description 6
- 238000011160 research Methods 0.000 description 5
- 238000013461 design Methods 0.000 description 4
- 239000004575 stone Substances 0.000 description 4
- 230000008901 benefit Effects 0.000 description 3
- 230000008859 change Effects 0.000 description 3
- 238000012986 modification Methods 0.000 description 3
- 230000004048 modification Effects 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 230000002708 enhancing effect Effects 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 238000007514 turning Methods 0.000 description 2
- 230000001720 vestibular Effects 0.000 description 2
- PEDCQBHIVMGVHV-UHFFFAOYSA-N Glycerine Chemical compound OCC(O)CO PEDCQBHIVMGVHV-UHFFFAOYSA-N 0.000 description 1
- 241001310793 Podium Species 0.000 description 1
- 241000219000 Populus Species 0.000 description 1
- 230000004075 alteration Effects 0.000 description 1
- 238000000540 analysis of variance Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000004888 barrier function Effects 0.000 description 1
- 238000010224 classification analysis Methods 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000008713 feedback mechanism Effects 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 235000021384 green leafy vegetables Nutrition 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 230000002452 interceptive effect Effects 0.000 description 1
- 238000004573 interface analysis Methods 0.000 description 1
- 238000007726 management method Methods 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 230000004630 mental health Effects 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 230000007480 spreading Effects 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 230000017260 vegetative to reproductive phase transition of meristem Effects 0.000 description 1
- 230000000007 visual effect Effects 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Classifications
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q10/00—Administration; Management
- G06Q10/06—Resources, workflows, human or project management; Enterprise or organisation planning; Enterprise or organisation modelling
- G06Q10/063—Operations research, analysis or management
- G06Q10/0631—Resource planning, allocation, distributing or scheduling for enterprises or organisations
- G06Q10/06315—Needs-based resource requirements planning or analysis
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q50/00—Information and communication technology [ICT] specially adapted for implementation of business processes of specific business sectors, e.g. utilities or tourism
- G06Q50/10—Services
- G06Q50/26—Government or public services
Landscapes
- Business, Economics & Management (AREA)
- Human Resources & Organizations (AREA)
- Engineering & Computer Science (AREA)
- Strategic Management (AREA)
- Tourism & Hospitality (AREA)
- Economics (AREA)
- General Business, Economics & Management (AREA)
- General Physics & Mathematics (AREA)
- Marketing (AREA)
- Entrepreneurship & Innovation (AREA)
- Educational Administration (AREA)
- Physics & Mathematics (AREA)
- Theoretical Computer Science (AREA)
- Development Economics (AREA)
- General Health & Medical Sciences (AREA)
- Health & Medical Sciences (AREA)
- Primary Health Care (AREA)
- Game Theory and Decision Science (AREA)
- Operations Research (AREA)
- Quality & Reliability (AREA)
- Road Paving Structures (AREA)
- Cultivation Of Plants (AREA)
Abstract
The present invention provides a kind of beside street in city greenery patches vegetation spatial configuration method that function is supported based on bio-diversity, the following steps are included: 1) greenbelt beside street is arranged in city, urban road land used is closed in the greenbelt beside street at least side, and the greenbelt beside street is inwardly successively arranged shrub area, arbor area by urban road land used；2) D is configuredt, calculate A；3) At, As and Ah are configured, R is calculated；4) arbor plant is configured, H is calculatedt.A kind of beside street in city greenery patches vegetation spatial configuration method for supporting function based on bio-diversity provided by the invention, the modes such as boundary's distance, the greening area coverage ratio in arbor area and the average height in arbor area are moved back by control arbor area, enhance the ability that greenbelt beside street resists external interference pressure, the safety for providing high canopy density for birds protects space, promote the bio-diversity of greenbelt beside street, the common thread that building harmony between man and nature coexists.
Description
Technical field
The invention belongs to the technical fields of landscape planning, are related to a kind of beside street in city that function is supported based on bio-diversity
Greenery patches vegetation spatial configuration method, and in particular to it is a kind of using specific indexes to beside street in city greenery patches vegetation carry out space configuration from
And the method for promoting beside street in city greenery patches bio-diversity.
Background technique
Urban Biodiversity is that various non-human organisms are regularly combined together and are embodied in city scope
The differential degree of the gene, species and urban ecological system that come is that natural background and the most important city of urban development are public
One of resource altogether.The variation of bio-diversity changes ecosystem processes and the ecosystem to the resistance of environmental change and tough
Property, it exerts far reaching influence to ecosystem service function, the health and happiness of the mankind is influenced further through feedback mechanism.
Since the whole world enters city century, Urban Biodiversity is unique two packing spaces that most of mankind can experience
Property.Greenbelt beside street is the essential supplement in Urban Parks as a part in urban green space system, with what be can not be substituted
Effect also promotes citizen's contact nature, to people while supporting Urban Natural ecological subsystem and a variety of species to inhabit habitat
Body physical and mental health generates positive influence.Therefore, the bio-diversity for how promoting beside street in city greenery patches seems particularly significant.
Greenbelt beside street refers to " be located at urban road land used except, relatively independent sheet of greenery patches ", including street and square green area,
Small-sized greenery patches along the street, street building vestibular greenery patches, the outer greenery patches band of boundary lines of roads etc..China is also once with petty street garden, residential block green belt, street
Head greenery patches, street corner petty street garden etc. define such land used.Similar concept is referred to as " block park " in Japan, in English, Mei Deng state quilt
Referred to as " Pocket Park (pocket park) ", " pocket park (mini-park) ", " micropolis public lawn (SPUGS,
Small Public Urban Green Spaces) " etc..
Although the ecological benefits that single greenbelt beside street is played are limited, in high density city, this small scale it is green
Ground still has and can not neglect to the local ecological environment weather of improvement, purification air, reduction noise, protection water and soil, offer oxygen etc.
Depending on effect；Importantly, the multiple small-sized greenery patchess for interspersing among city various regions are walked with other kinds of park green land and ecology
The validity and Connected degree of urban ecological net can be substantially improved in the combination of corridor, for particular organisms it is mobile provide foothold and
Netted alternate path becomes important sanctuary (Shelter) and mobile stepping-stone that biology has a rest and looks for food
(Stepping-stone), it is similarly of great significance to promotion Urban Biodiversity.
The existing a large amount of discussion of leisure, beautifying functions and its Environment Design in beside street in city greenery patches, and its ecological functions is outstanding
It is that bio-diversity supports function to be but usually ignored, and the beside street in city research greenly for focusing bio-diversity problem is considerably less
See.
Summary of the invention
In view of the missing of existing bio-diversity Correlative plan index described above, the purpose of the present invention is to provide one kind
The beside street in city greenery patches vegetation spatial configuration method that function is supported based on bio-diversity does biology for solving to reduce
Disturb, the beside street in city greenery patches that promotes bio-diversity and construct harmony between man and nature coexisted environment the problem of.
In order to achieve the above objects and other related objects, first aspect present invention provides a kind of based on bio-diversity support
The beside street in city greenery patches vegetation spatial configuration method of function, comprising the following steps:
1) greenbelt beside street is set in city, and urban road land used is closed in the greenbelt beside street at least side, by the street
Greenery patches is inwardly successively arranged shrub area, arbor area by urban road land used；
2) D is configuredt, formula (1) is complied with,
The formula (1) are as follows: A=Dt/D
Wherein, DtBoundary's distance, m are moved back for arbor area；A moves back boundary for the high forest of greenbelt beside street and leads；D is the depth of greenbelt beside street
Distance, m；
3) At, As and Ah are configured, formula (2) are complied with,
The formula (2) are as follows: R=(At+As+Ah)/Sq
Wherein, R is the greening area coverage ratio in arbor area；At is the arbor area coverage in arbor area, m2；As is arbor
Shrub area coverage in area, m2；Ah is the Land cover area in arbor area, m2；SqFor the area in arbor area, m2；
4) arbor plant is configured, formula (3) are complied with,
The formula (3) are as follows: Ht=∑ (at×ht)/∑ht
Wherein, HtFor the average height in arbor area, m；htFor the height of t kind arbor, m；atFor the plant of t kind arbor
Number.
Preferably, in step 1), the urban road land used is selected from through street, trunk roads, secondary distributor road, branch and its intersection
Mouthful land used, driveway, pavement, dividing strip, one or more combinations in greenery patches.
It is highly preferred that the driveway includes non-motorized lane and car lane.
Preferably, in step 1), the edge that the greenbelt beside street closes on urban road land used easily forms the dry of mankind's activity
Disturb interface.The urban road land used can form mankind's activity interference to greenbelt beside street.
Preferably, in step 1), the greening planted in the shrub area is ground quilt and shrub.With shrub in the shrub area
Mainly to plant trees.The boundary that urban road land used is closed in the shrub area easily forms the interference interface of mankind's activity, described
It is interfered vulnerable to extraneous mankind's activity in shrub area.
Preferably, in step 1), when the shrub area is located at the greenbelt beside street area in the sight triangle at corner
In domain, height≤0.7m of all greenings in the shrub area.All greenings (including ground quilt and filling in the shrub area
Wood), thinly scattered open afforestation effect is formed, sight triangle principle is met.
The sight triangle (sight triangle) refers at grade crossing, enters crossing row by a road
The intersection point of the outermost lane middle line and the innermost lane middle line of road intersection of sailing direction is vertex, and two lane middle lines are each
Provide that the length of speed stopping sight distance is both sides, composed triangle by it.
The sight triangle principle refers to, in order to close on greenbelt beside street two intersection urban roads on through vehicles
There is safe stopping sight distance, guarantees that the sight of driver when Road turnings is not blocked, the street within the scope of sight triangle
The plant height in other greenery patches is unsuitable excessively high, cannot there is excessively high barrier in sight triangle, such as building, structures, wide
Board etc. is accused, to form thinly scattered open afforestation effect.
Preferably, in step 1), the greening planted in the arbor area is ground quilt, shrub and arbor.In the arbor area
It is main plantation trees with arbor.
It is highly preferred that the arbor selects food-borne indigenous plant, the arbor species should be preced with big shady dense.
It is highly preferred that quilt, shrub and arbor are planted using multilayer structure describedly, ground quilt, shrub and matching for arbor are set low
Middle height combines.
Preferably, in step 1), attached green space is equipped between all kinds of communities in arbor area and city.The attached green space is formed
Abutment.All kinds of communities in city include but is not limited to one of residential area, business district or shopping centre or multiple combinations.
Preferably, in step 2), the boundary edge that moves back in the arbor area forms continuous interface using dense planting gimmick.
Preferably, in step 2), boundary's distance of moving back in the arbor area refers to and closes on urban road rand by greenbelt beside street
Edge is to the horizontal distance between the boundary in arbor area.The boundary in the arbor area refers to arbor area close to the head of urban road land used
The continuous arbor interface of layer.
Preferably, in step 2), the depth distance of the greenbelt beside street refers to by greenbelt beside street one side edge to the other side
The horizontal distance at edge.
Preferably, in step 2), as depth distance D≤6m of the greenbelt beside street, the high forest moves back boundary and leads A≤0.7；
As the depth distance D > 6m and D≤15m of the greenbelt beside street, the high forest moves back boundary and leads A≤0.6；
As the depth distance D > 15m of the greenbelt beside street, the high forest moves back boundary and leads A≤0.5.
The high forest moves back boundary and leads the ability that reflection greenbelt beside street resists mankind's activity interference.
Preferably, greening area coverage ratio R >=2 in step 3), in the arbor area.
Preferably, the average height H in step 4), in the arbor areat≥12m。
Second aspect of the present invention provides a kind of beside street in city greenery patches, is configured and is obtained by the above method.
As described above, a kind of beside street in city greenery patches vegetation space for supporting function based on bio-diversity provided by the invention
Configuration method has the advantages that
(1) a kind of beside street in city greenery patches vegetation space configuration side that function is supported based on bio-diversity provided by the invention
Method is configured by the proportional space to beside street in city greenery patches vegetation, and shrub area, arbor area is arranged, makes greenbelt beside street as birds
The transfer " stepping-stone " of equal Urban Wildlifes provides abundant safety by dense branches and leaves for Urban Wildlifes such as birds
Inhabit protect space, increase the avian species richness of greenbelt beside street.
(2) a kind of beside street in city greenery patches vegetation space configuration side that function is supported based on bio-diversity provided by the invention
Method, the high forest by the way that greenbelt beside street is arranged move back by way of boundary leads, rational deployment, in the convenience for guaranteeing that landscape and crowd use
While, the interference that periphery function is formed a team with road to biology is reduced, enhancing greenbelt beside street is resisted outer as small-sized greenery patches habitat
The level of boundary's interference pressure.
(3) a kind of beside street in city greenery patches vegetation space configuration side that function is supported based on bio-diversity provided by the invention
Method in the micro- update in city, by the transformation to greenbelt beside street, makes birds and other from the visual angle of landscape planning design
Biology has more places that can stop in city, being capable of effective protection bio-diversity, promotion ecosystem service function
The city space of optimization generates, and provides foundation for bio-diversity is protected and promoted from landscape planning design angle, can construct
The common thread that harmony between man and nature coexists.
Detailed description of the invention
The high forest that Fig. 1 is shown as one of present invention beside street in city greenery patches moves back the planar structure schematic diagram that boundary is led.
The high forest that Fig. 2 is shown as one of present invention beside street in city greenery patches moves back the schematic perspective view that boundary is led.
Fig. 3 is shown as the bird kind number comparison schematic diagram in one of present invention beside street in city greenery patches Yu other greenery patchess.
Fig. 4 is shown as the bird abundance comparison schematic diagram in one of present invention beside street in city greenery patches Yu other greenery patchess.
Fig. 5 is shown as the fluctuating range of one of present invention beside street in city greenery patches avian species richness and other greenery patchess
With the comparison schematic diagram of average value.
Fig. 6 is shown as the fluctuating range of one of present invention beside street in city greenery patches Avian diversity index and other greenery patchess
With the comparison schematic diagram of average value.
Fig. 7 is with being shown as the field of investigation of survey region, greenbelt beside street sample and control group greenery patches position view.
Fig. 8 is shown as greenbelt beside street along century avenue and selects position view with studying sample in detail.
Fig. 9 is shown as greenbelt beside street classification and interface analysis schematic diagram along century avenue.
Figure 10 is shown as along century avenue greenbelt beside street species richness and compared with adjacent settlement species richness
Schematic diagram.
Figure 11 is shown as greenbelt beside street avian species richness and interference/abutment along century avenue and compares schematic diagram.
Figure 12 with being shown as sample 21 with sample 5 vegetation space configuration comparison schematic diagram a, b, wherein Figure 12 a for sample 21
Vegetation space configuration figure, Figure 12 b for sample 5 vegetation space configuration figure.
Figure 13 is shown as greenbelt beside street and sight triangle relation schematic diagram.
Appended drawing reference
DtBoundary's distance is moved back in arbor area
The depth distance of D greenbelt beside street
Specific embodiment
The present invention is further explained combined with specific embodiments below, it should be appreciated that these embodiments are merely to illustrate the present invention
Rather than it limits the scope of the invention.
Illustrate embodiments of the present invention below by way of specific specific example, those skilled in the art can be by this specification
Other advantages and efficacy of the present invention can be easily understood for disclosed content.The present invention can also pass through in addition different specific realities
The mode of applying is embodied or practiced, the various details in this specification can also based on different viewpoints and application, without departing from
Various modifications or alterations are carried out under spirit of the invention.
Embodiment 1
Greenbelt beside street is set in city, greenbelt beside street is located at except urban road land used, it is relatively independent in flakes, side or
Urban road land used is closed in more sides, and all kinds of community directions along urban road land used to surrounding are inwardly successively arranged shrub area, Qiao
The wooden area.Greenbelt beside street includes but is not limited to street and square green area, small-sized greenery patches along the street, street building vestibular greenery patches, boundary lines of roads
Outer greenery patches band etc. generally also can define such land used with petty street garden, residential block green belt, street greens, street corner petty street garden etc..City road
Road land used is selected from through street, trunk roads, secondary distributor road, branch and its intersection land used, driveway (including non-motorized lane and motor-driven
Lane), pavement, dividing strip, one or more combinations in greenery patches.It is specifically shown in Fig. 1,2.
The greening planted in shrub area is ground quilt and shrub, and the shrub area of neighbouring urban road land used is vulnerable to extraneous vehicle
With the interference of mankind's activity.When shrub area is located in the greenbelt beside street region in the sight triangle at corner, shrub area
Height≤0.7m of interior all greenings.The greening height planted in shrub area meets sight triangle principle.
Specifically, due to greenbelt beside street neighbour's urban road land used, in plants configuration it has to be ensured that two
Through vehicles have safe stopping sight distance on road intersection, with the proviso that must assure that the sight of driver when Road turnings not
It is blocked.Sight triangle (sight triangle) refers at grade crossing, enters crossing traveling by a road
The outermost lane middle line in direction and the intersection point of the innermost lane middle line of road intersection are vertex, and two lane middle lines are respectively pressed
It provides that the length of speed stopping sight distance is both sides, composed triangle.Shrub area within the scope of sight triangle, it is green
Change height no more than 0.7 meter, answers the ground cover plants such as turf plant, grove and flowering shrub can be interspersed on lawn, it is thinly scattered to be formed
Open afforestation effect.It is specifically shown in Figure 13.
Attached green space is equipped between all kinds of communities in arbor area and city.All kinds of communities in city include but is not limited to residential area,
One of business district or shopping centre or multiple combinations.
The greening planted in arbor area is ground quilt, shrub and arbor.Arbor selects food-borne indigenous plant, and arbor species answer
Hat is big shady dense.Ground is planted by, shrub and arbor using multilayer structure, and ground is set low middle height and combined by matching for, shrub and arbor.It is tall
The boundary edge that moves back in the wooden area forms continuous interface using dense planting gimmick.
Configure Dt, comply with formula (1): A=Dt/ D, wherein DtBoundary's distance, m are moved back for arbor area；A is green by street
The high forest on ground moves back boundary and leads；D is the depth distance of greenbelt beside street, m.As depth distance D≤6m of the greenbelt beside street, Qiao
Lin Tui circle leads A≤0.7；As the depth distance D > 6m and D≤15m of the greenbelt beside street, the high forest moves back boundary and leads A≤0.6；
As the depth distance D > 15m of the greenbelt beside street, the high forest moves back boundary and leads A≤0.5.
At, As and Ah are configured, is complied with formula (2): R=(At+As+Ah)/Sq, wherein R is the greening in arbor area
Area coverage ratio；At is the arbor area coverage in arbor area, m2；As is the shrub area coverage in arbor area, m2；Ah is Qiao
Land cover area in the wooden area, m2；SqFor the area in arbor area, m2.The greening area coverage being further defined in arbor area
Than R >=2.
Arbor plant is configured, formula (3): H are complied witht=∑ (at×ht)/∑ht, wherein htFor t kind arbor
Highly, m；atFor the plant number of t kind arbor.The average height H being further defined in arbor areat≥12m。
Embodiment 2
Using greenbelt beside street along the century avenue of Pudong New Area, Shanghai as research object, century avenue is bright west from east
Pearl is the axis of a connection big terrestrial reference node in city two to the east of Century Park.
The range of this research includes century avenue 100 meters of high section two sides and complete neighbour from Xiaolujiazui Region to poplar,
And beautiful curb line and Century Park amount to 51 plot to the neighbour in street.The sample of greenbelt beside street is equipped in survey region
23, wherein there is 9, triangle street corner greenery patches in the special-shaped intersection of century avenue and peripheral path, they are in greening management
It is noted as in " interim greenery patches ", but in order to which landscape effect along the street has carried out preferable artificial vegetation's Landscape arrangement, this kind of greenery patches rule
Mould is big compared with general greenbelt beside street, daily to be safeguarded and trimmed by afforesting administrative department, experienced certain vegetation in the past 20 years
Succession.Remaining 7 are the petty street garden on the pavement of century avenue north side, and each about 180m long 20m wide is enclosed with white white washed wall,
Vegetation is more single in garden；Separately there is the residential area Linear Green Space along the street at 5 for short of width 5m, at 1 at podium and 1 between Business Building
Greenery patches (table 1).
For the ease of making comparisons with periphery greenery patches, research with also setting 62 other types greenery patches samples as a control group,
Wherein Comprehensive Park 1, Community Park 3, Linear Park 4, productive plantation area 1, residential green space 21, communal facility greenery patches
21, Road Green Space 10, wetland 1 (Fig. 7).
The type in all kinds of greenbelt beside street areas of 1 survey region of table and adjacent plot
For all kinds of greenbelt beside streets in the studies above region, Investigation on Birds is carried out in October, 2015 in November, 2014-, often
Moon investigation is primary, investigates 12 times altogether.It monthly investigates and concentrates on the first tenday period of a month as far as possible, be typically chosen in fine early morning at weekend, and
It is determined as winter 7:00-10:00, spring, autumn 6:30-9:30, summer 6:00-9:00 according to sunrise time.Investigation uses sample
Collimation method carries out.When investigation, is advanced with the travel speed of 1.5km/h, stopped according to the scale on sample ground and habitat speciality in each sample
Stay differ within 5-15 minutes, using 8-10 times of binoculars, the type for the wild birds seen and heard in record sample ground,
Quantity etc..According to birds quantity and classification data that field measurement inquiry agency records, bird abundance, the species on each sample ground are calculated
Richness, diversity indices.Bird abundance is with birds quantity (only/hm in unit sample area2) indicate.Diversity indices
It is calculated using Shannon-Wiener exponential formula, i.e. H ': one Σ PilogPi, wherein PiFor species i individual amount with
The ratio between all total Number of Species.It is right using Microsoft Excel and IBM SPSS19.0FOR WINDOWS statistical analysis software
Greenbelt beside street is compared with bird kind quantity, density and the diversity in other greenery patchess, is analyzed using ANOVA and is carried out the significance of difference
It examines, and inquires into the environment influent factor that birds bio-diversity supports function.
By calculated result it is found that investigation records is arrived in whole region city wild birds 10,231 are secondary, according to " in
The classification of state birds and distribution register " (third edition), it is subordinate to 47 kinds of 8 mesh, 25 section, the bird kind quantity of different greenlands has extremely significant difference
Different (P=4.86E-6 < 0.01).Wherein greenbelt beside street observes birds 21 kinds of 14 section of totally 3 mesh, and kind number accounting is 44.68%, high
In productive plantation area (16 kinds) and Comprehensive Park (16 kinds), slightly below communal facility greenery patches (22 kinds) and Linear Park (24 kinds) (see
Fig. 3).
Bird abundance between all kinds of greenery patchess also has extremely significant sex differernce (P=0.009 < 0.01).Greenbelt beside street unit plane
Long-pending bird abundance is higher than Comprehensive Park, Community Park, Linear Park, productive plantation area, residential green space, communal facility, illustrates street
The area in other greenery patches is although small, but density may be high, i.e. the birds quantity of unit area attraction is possible more (Fig. 4), therefore,
Greenbelt beside street equally plays important supporting function in terms of Avian diversity.
For the species richness of single greenbelt beside street between 1~10, average value 5, diversity indices fluctuates width simultaneously
It spends all larger.Whole species richness is compared, the whole species richness of greenbelt beside street is higher, but single plot is lower, various regions
The Diversity of block is all larger, that is to say, that bird kind limited amount that each greenbelt beside street can be attracted to but different, this
It tentatively illustrates that the landscape otherness of the greenbelt beside street of survey region is larger, there is different lifes to the different types of birds in city
Object diversity supports function (Fig. 5,6).
In addition, using avian species richness as Comparative indices, residential area that comparison greenbelt beside street and periphery directly border on,
The difference in business area greenery patches, as shown in fig. 7, research discovery: other than the sample ground that 4 can not compare, 19 comparative samples
In, the avian species richness on only 7 sample ground is lower than adjacent plot greenery patches, wherein be century avenue petty street garden (2,9) at 2,4
Place is the unilateral residential area for adjoining street Linear Green Space (15,17,18,19) along the street, separately there is the triangle for adjoining business area at 1
Shape street corner greenery patches (20).The above two are interfered more and vegetation relatively single by stream of people's wagon flow, sample 20 area it is smaller and adjacent
Business area ratio of green space it is not high, it is limited to the attraction of birds.The avian species richness on another 12 samples ground is all higher than neighbour
Earthing block, and it is higher (table 2) with the quantity for abutting the identical bird kind that plot greenery patches is recorded, further prove the region
Greenbelt beside street has the function of that certain birds bio-diversity is supported.In terms of its similitude with adjacent block greenery patches birds, street
Other greenery patches also has certain " stepping-stone " function of spreading outward from the abundant area of Avian diversity around.
2 greenbelt beside street of table is adjacent the avian species richness and similarity system design in block greenery patches
Embodiment 3
7 pieces of triangle greenbelt beside streets are selected as the sample studied in detail in 23 pieces of greenbelt beside streets in example 2, are selected
Foundation are as follows: (1) (area 1,500m of certain scale2More than), to form relatively complicated biocoene；(2) with
Residential area borders on, to examine or check these greenery patchess to the reinforcing of adjacent settlement Bird diversity or to weaken effect, by selected street
All two class Residential lands used similar with mining inetesity are bordered in greenery patches, have evaded adjacent development pattern of residential district intensity difference bring
It influences；(3) at least a line bound pair connects public pavement or driveway, to examine the influence of mankind's interfering activity.It is selected
The greenery patches position selected is as shown in Figure 8.
According to the spatial relationship of 7 pieces of triangle greenbelt beside streets and road and periphery plot, this they can be divided into most end formula
2 groups of greenbelt beside street (sample 3,5,6,8,12) and embedded greenbelt beside street (sample 11,21).Interference circle of formula greenbelt beside street is held to the greatest extent
Face is greater than abutment, and the interference interface of embedded greenbelt beside street is less than abutment (Fig. 9).
As shown in Figure 10, analysis is the result shows that the species of the slightly above adjacent settlement of the avian species richness of greenbelt beside street are rich
Fu Du, but do not have significant difference (P=0.192 > 0.05).The species on 3,5,6,8 four bigger sample ground of greenery patches plaque area
Than 11,12,21 3 samples of richness ground few half or so, and about the same with adjacent settlement, then three greenbelt beside streets
Species richness is substantially better than adjacent settlement, i.e., has bigger support to the Bird diversity of whole block.To vegetation knot
Structure the study found that the species richness and vegetative coverage area, height and type of 7 greenbelt beside streets also without more apparent
It is associated with influential effect.
Interference interface and the abutment prospected based on AutoCAD topographic map and scene and measure greenbelt beside street are studied, and
Ratio between the two is calculated, being greater than 1 is that interference effect is greater than adjacent influence, on the contrary less than 1.Result of study discovery, does
Disturb/mean value of the species richness of greenbelt beside street of the abutment less than 1 and intermediate value (7) be all larger than interference/abutment greater than 1
Greenbelt beside street (mean value=6.33, intermediate value=5) (Figure 11), although do not have significant difference (P=0.565 > 0.05), it is whole
For body, shorten interference boundary as far as possible and increase adjacent boundary, i.e., embedded greenbelt beside street is set as far as possible rather than holds formula to the greatest extent
Greenbelt beside street, it is relatively more advantageous for the Bird diversity of greenbelt beside street.
In above-mentioned 7 plot, sample 3,5 with sample 11,21 interference/abutment ratio it is substantially suitable, but species are abundant
Degree but differs half, and the avian species richness of the latter is all higher than adjacent settlement, and the former remains basically stable.Further analysis
It was found that this may be related with the vegetation space configuration in two class greenery patchess.The vegetation space configuration canopy density of the latter are higher, and the first floor
The planting location of high megaphanerophyte is closer to interference boundary, therefore tall and big arborous layer forms certain resist to extraneous mankind's activity
Interference performance, and space is inhabited by dense branches and leaves for what birds provided abundant safety.It is specifically shown in Figure 12 a and Figure 12 b.
In conclusion a kind of beside street in city greenery patches vegetation space for supporting function based on bio-diversity provided by the invention
Configuration method moves back boundary's distance, the greening area coverage ratio in arbor area and the average height in arbor area by control arbor area
Etc. modes, enhancing greenbelt beside street resist external interference pressure ability, for birds provide high canopy density safety protection space, mention
Rise the bio-diversity of greenbelt beside street, the common thread that building harmony between man and nature coexists.So the present invention effectively overcomes
Various shortcoming in the prior art and have high industrial utilization value.
The above-described embodiments merely illustrate the principles and effects of the present invention, and is not intended to limit the present invention.It is any ripe
The personage for knowing this technology all without departing from the spirit and scope of the present invention, carries out modifications and changes to above-described embodiment.Cause
This, institute is complete without departing from the spirit and technical ideas disclosed in the present invention by those of ordinary skill in the art such as
At all equivalent modifications or change, should be covered by the claims of the present invention.
Claims (10)
1. a kind of beside street in city greenery patches vegetation spatial configuration method for supporting function based on bio-diversity, comprising the following steps:
1) greenbelt beside street is set in city, and urban road land used, the greenbelt beside street are closed in the greenbelt beside street at least side
Shrub area, arbor area are inwardly successively arranged by urban road land used；
2) D is configuredt, formula (1) is complied with,
The formula (1) are as follows: A=Dt/D
Wherein, DtBoundary's distance is moved back for arbor area；A moves back boundary for the high forest of greenbelt beside street and leads；D is the depth distance of greenbelt beside street；
3) At, As and Ah are configured, formula (2) are complied with,
The formula (2) are as follows: R=(At+As+Ah)/Sq
Wherein, R is the greening area coverage ratio in arbor area；At is the arbor area coverage in arbor area；As is in arbor area
Shrub area coverage；Ah is the Land cover area in arbor area；SqFor the area in arbor area；
4) arbor plant is configured, formula (3) are complied with,
The formula (3) are as follows: Ht=∑ (at×ht)/∑ht
Wherein, HtFor the average height in arbor area；htFor the height of t kind arbor；atFor the plant number of t kind arbor.
2. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, which is characterized in that in step 1), the urban road land used is selected from through street, trunk roads, secondary distributor road, branch and its friendship
Prong land used, driveway, pavement, dividing strip, one or more combinations in greenery patches.
3. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, which is characterized in that in step 1), the greening planted in the shrub area is ground quilt and shrub.
4. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, which is characterized in that in step 1), when the shrub area is located at the greenbelt beside street area in the sight triangle at corner
In domain, height≤0.7m of all greenings in the shrub area.
5. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, which is characterized in that in step 1), the greening planted in the arbor area is ground quilt, shrub and arbor.
6. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 5
Method, which is characterized in that the arbor selects food-borne indigenous plant, and the arbor species should be preced with big shady dense.
7. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, which is characterized in that in step 2), as depth distance D≤6m of the greenbelt beside street, the high forest move back boundary lead A≤
0.7；As the depth distance D > 6m and D≤15m of the greenbelt beside street, the high forest moves back boundary and leads A≤0.6；It is green by the street
When the depth distance D > 15m on ground, the high forest moves back boundary and leads A≤0.5.
8. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, in step 3), greening area coverage ratio R >=2 in the arbor area.
9. a kind of beside street in city greenery patches vegetation space configuration for supporting function based on bio-diversity according to claim 1
Method, which is characterized in that the average height H in step 4), in the arbor areat≥12m。
10. a kind of beside street in city greenery patches, which is characterized in that -9 any described one kind are based on two packing spaces according to claim 1
Property support function beside street in city greenery patches vegetation spatial configuration method configure obtain.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201811637697.8A CN109544045B (en) | 2018-12-29 | 2018-12-29 | Urban street green land vegetation space configuration method based on biodiversity support function |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201811637697.8A CN109544045B (en) | 2018-12-29 | 2018-12-29 | Urban street green land vegetation space configuration method based on biodiversity support function |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN109544045A true CN109544045A (en) | 2019-03-29 |
| CN109544045B CN109544045B (en) | 2021-06-15 |
Family
ID=65831310
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201811637697.8A Expired - Fee Related CN109544045B (en) | 2018-12-29 | 2018-12-29 | Urban street green land vegetation space configuration method based on biodiversity support function |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN109544045B (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110249893A (en) * | 2019-07-19 | 2019-09-20 | 中国科学院地理科学与资源研究所 | A kind of greenbelt system of group of cities inside ecology corridor |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20100026229A (en) * | 2008-08-29 | 2010-03-10 | 부경대학교 산학협력단 | Method and system for compensating normalized distribution vegetation index |
| CN102635075A (en) * | 2012-05-10 | 2012-08-15 | 南京林业大学 | Plant configuration used for urban road traffic noise reduction |
| CN105580627A (en) * | 2015-12-21 | 2016-05-18 | 广西丰景园林建设工程有限公司 | Greening method for improving urban rainwater interception function |
| CN107950267A (en) * | 2017-10-11 | 2018-04-24 | 深圳市城市规划设计研究院有限公司 | A kind of construction method of the multifarious Urban Parks of imitative natural biology |
-
2018
- 2018-12-29 CN CN201811637697.8A patent/CN109544045B/en not_active Expired - Fee Related
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20100026229A (en) * | 2008-08-29 | 2010-03-10 | 부경대학교 산학협력단 | Method and system for compensating normalized distribution vegetation index |
| CN102635075A (en) * | 2012-05-10 | 2012-08-15 | 南京林业大学 | Plant configuration used for urban road traffic noise reduction |
| CN105580627A (en) * | 2015-12-21 | 2016-05-18 | 广西丰景园林建设工程有限公司 | Greening method for improving urban rainwater interception function |
| CN107950267A (en) * | 2017-10-11 | 2018-04-24 | 深圳市城市规划设计研究院有限公司 | A kind of construction method of the multifarious Urban Parks of imitative natural biology |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110249893A (en) * | 2019-07-19 | 2019-09-20 | 中国科学院地理科学与资源研究所 | A kind of greenbelt system of group of cities inside ecology corridor |
| CN110249893B (en) * | 2019-07-19 | 2024-06-04 | 中国科学院地理科学与资源研究所 | Greenbelt system of ecological corridor inside city group |
Also Published As
| Publication number | Publication date |
|---|---|
| CN109544045B (en) | 2021-06-15 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Ignatieva et al. | Planning and design of ecological networks in urban areas | |
| Haase et al. | Green infrastructure in post-socialist cities: Evidence and experiences from Eastern Germany, Poland and Russia | |
| Sangwan et al. | Urban green spaces prospects and retrospect’s | |
| Sisman | Pedestrian zones | |
| CN109544045A (en) | A kind of beside street in city greenery patches vegetation spatial configuration method for supporting function based on bio-diversity | |
| Barchetta et al. | The variety of urban green spaces and their diverse accessibility | |
| Nilufar | Preserving open space for livability of Dhaka | |
| Polat et al. | The contributions of urban landscape to urban life | |
| Akmar et al. | Local governments and urban ecology: Planning and practice examples from Africa, Asia, and Europe | |
| Smoliar et al. | Urban green zones planning concept and ecological functionality (through the example of Poltava, Ukraine) | |
| Gan | Urban Biodiversity and Built Environment: Case Study of Shanghai | |
| Li | Green Networks: Guidelines for Developing Taipei as an Eco-City Based on Case Studies of Three Greenways in Sheffield | |
| Tasnim | Study on potential integration of greenway on urban street canyon at planned residential area of Dhaka city | |
| Yue et al. | Analysis of the functional manifestation of plant landscape management on urban roads | |
| Johansen | Understanding of Green Infrastructure and implications for urban planning in the Mexican city of Culiacán | |
| Comey | Houston: Tentative Plans for Its Development; Report to the Houston Park Commission | |
| Schulte | A City Under the Sedums: Ecosystem Services and Adoption of Vegetated Roofs in Atlanta, Georgia | |
| Shofwan et al. | Identification Of Typology Of Green Open Space (RTH) In The Sidoarjo Mud Disaster Area | |
| Omonova | THE IMPORTANCE OF LANDSCAPE ORGANIZATION IN ENVIRONMENTAL ENVIRONMENT OF SOUTHERN CITIES | |
| 조원희 | Urban Forest Edge as an Approach Towards Sustainability: Focus on Onsu-dong, Guro-gu, Seoul | |
| Utomo et al. | Designing Green Space for Improving the Quality of Streetscape of Rungkut Madya Surabaya | |
| Gan | Urban biodiversity and built environment | |
| Syed | Landscape design guidelines for Karachi City, Pakistan | |
| Önder et al. | The Contributions of Urban Landscape to Urban Life | |
| Cai | Assessment of Ecosystem Services of Urban Green Space as a Tool for Sustainable Urban Development: The Case of Xi’an, China |
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 | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20210615 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |