CN110378576A - The quantification detection method of urbanization vegetation effect effective distance - Google Patents

The quantification detection method of urbanization vegetation effect effective distance Download PDF

Info

Publication number
CN110378576A
CN110378576A CN201910587655.6A CN201910587655A CN110378576A CN 110378576 A CN110378576 A CN 110378576A CN 201910587655 A CN201910587655 A CN 201910587655A CN 110378576 A CN110378576 A CN 110378576A
Authority
CN
China
Prior art keywords
vegetation index
city
vegetation
cities
areas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201910587655.6A
Other languages
Chinese (zh)
Inventor
杜加强
付青
全占军
吴金华
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Chinese Research Academy of Environmental Sciences
Chinese Academy of Environmental Sciences
Original Assignee
Chinese Academy of Environmental Sciences
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Chinese Academy of Environmental Sciences filed Critical Chinese Academy of Environmental Sciences
Priority to CN201910587655.6A priority Critical patent/CN110378576A/en
Publication of CN110378576A publication Critical patent/CN110378576A/en
Pending legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G06COMPUTING; CALCULATING OR COUNTING
    • G06QINFORMATION 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
    • G06Q10/00Administration; Management
    • G06Q10/06Resources, workflows, human or project management; Enterprise or organisation planning; Enterprise or organisation modelling
    • G06Q10/063Operations research, analysis or management
    • G06Q10/0639Performance analysis of employees; Performance analysis of enterprise or organisation operations
    • GPHYSICS
    • G06COMPUTING; CALCULATING OR COUNTING
    • G06QINFORMATION 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
    • G06Q50/00Systems or methods specially adapted for specific business sectors, e.g. utilities or tourism
    • G06Q50/10Services
    • G06Q50/26Government or public services
    • GPHYSICS
    • G06COMPUTING; CALCULATING OR COUNTING
    • G06VIMAGE OR VIDEO RECOGNITION OR UNDERSTANDING
    • G06V20/00Scenes; Scene-specific elements
    • G06V20/10Terrestrial scenes
    • G06V20/176Urban or other man-made structures
    • GPHYSICS
    • G06COMPUTING; CALCULATING OR COUNTING
    • G06VIMAGE OR VIDEO RECOGNITION OR UNDERSTANDING
    • G06V20/00Scenes; Scene-specific elements
    • G06V20/10Terrestrial scenes
    • G06V20/188Vegetation

Abstract

The invention discloses the quantification detection methods of urbanization vegetation effect effective distance, comprising: establishes the data set of city/group of cities many years space and time continuous remote sensing vegetation index;The newest range in city/group of cities built-up areas is extracted based on remotely-sensed data;The buffer area spacing of spatial resolution setting built-up areas based on remote sensing vegetation index;The many years for calculating city/group of cities built-up areas and buffer area are averaged vegetation index;Zoning is averaged vegetation index variation tendency;The vegetation index variation tendency of city/group of cities built-up areas and buffer area is calculated by pixel;Calculate the vegetation index significant changes area ratio of city/group of cities built-up areas and buffer area;Three index dynamic changing curves are established, judge to influence effective distance.The above method can be realized urban construction and detect to the quantification of Vegetation Effect effective distance, easy to use, robustness is good, precision is high, provide direct technology support for the city ecological environment protection, urban landscaping, restoration of the ecosystem, ecological surveillance etc..

Description

The quantification detection method of urbanization vegetation effect effective distance
Technical field
The present invention relates to a kind of remotely-sensed data data analysis technique fields, have especially with regard to a kind of urbanization vegetation effect Imitate the quantification detection method of distance.
Background technique
Urbanization produces far-reaching influence to ecosystems services and function, bio-diversity etc., it is considered to be One of main drive of Ecosystem Changes.There are " space spills-over effects " in influence of the urbanization to the ecosystem, i.e. city Change process not only will affect ecological environment inside completed region of the city, can also influence built-up areas periphery ecology ring to a certain extent Border.Therefore, quantification urban construction is on effective influence distance of the ecosystem, for urban development planning, ecological environmental protection And the work such as town development boundary, ecological protection red line delimited with highly important realistic price and practice significance.
Vegetation is the most important component part of terrestrial ecosystems, formation and performance for ecosystems services and function With important supporting role.As the primary producer of food chain bottom end, vegetation can change solar energy by photosynthesis For chemical energy, energy is provided for organism including humans;By respiration, transpiration and change the surface reflection of light Rate, fundamentally adjust earth's surface energy balance, water circulation and biogeochemical cycle, and for other biological provide food with Habitat.In recent years, global environmental change is being interrogated changes landing field vegetation state fastly, so as to the function of earth system Offer with ecosystems services has an impact.As the composite measurement of ecological functions, the change in time and space of vegetation productivity for Terrestrial Carbon Sink estimation, natural resource management, ecological study are extremely important, and the variation of monitoring vegetation growth has understood its origin cause of formation Become history one of the critical issue of decades whole world change.NDVI(Normalized Difference Vegetation Index, normalized site attenuation) it is considered as that vegetation productivity effectively acts on behalf of the best of index and vegetation growth status Characteristic index is one of key metrics index of ecological degradation, very extensive concern has been obtained from region to Global Scale And application.EVI (Enhanced Vegetation Index, enhancement mode meta file) is to improve to propose on the basis of NDVI , not only allow for Soil Background influence, also according to the impact factor that atmospheric correction is included, for example, atmospheric molecule, aerosol, The problems such as factors such as Bao Yun, steam and ozone carry out comprehensive atmospheric correction, have handled soil, atmosphere and saturation degree, to vegetation With higher sensitivity and superiority.Therefore, ecosystem situation is represented using vegetation indexs such as NDVI, EVI is more Current, generally acknowledged method.
Currently, urbanization focuses mostly on to the research of Vegetation Effect raw in fitting urbanization process and vegetation coverage, vegetation Relationship between force of labor, vegetation phenology, forest loss, revegetation, ecosystems services and its value etc., then judges city The vegetation of change, ecological effect.Part research thinks that influence of the urban construction to vegetation, ecology is not solely restricted to built-up areas, right Its periphery also has a certain impact, and has application from completed region of the city periphery 5-10km and 100km, but it is mostly qualitative to influence distance Judgement.
It can be seen that the detection method for influencing effective distance to the ecosystem in relation to urbanization at present extremely lacks, it is different The result that expert obtains is inconsistent, and accuracy and accuracy are inevitably present uncertainty, can also deposit in application process In certain problem.
The present invention is based on long-term sequence remote sensing of vegetation data, by establishing multiple indexs, multiple dimensioned, multizone to score The method of analysis discloses urbanization process to Vegetation Effect with the attenuation process of distance, reaches quantification urbanization to Vegetation Effect The purpose of effective distance.
The information disclosed in the background technology section is intended only to increase the understanding to general background of the invention, without answering When being considered as recognizing or imply that the information constitutes the prior art already known to those of ordinary skill in the art in any form.
Summary of the invention
The purpose of the present invention is to provide a kind of quantification detection methods of urbanization vegetation effect effective distance, can Realize that urban construction detects the quantification of Vegetation Effect effective distance, it is easy to use, robustness is good, precision is high.
To achieve the above object, the present invention provides a kind of quantification detection sides of urbanization vegetation effect effective distance Method, the quantification detection method are based on long-term sequence remote sensing of vegetation data, comprising the following steps:
S01: according to Remote Sensing Products or remote sensing image establishes city and/or many years space and time continuous remote sensing vegetation of group of cities refers to Several data sets;
S02: the newest range in built-up areas of city and/or group of cities is extracted based on remotely-sensed data;
S03: the spatial resolution based on remote sensing vegetation index sets the buffer area spacing of the built-up areas, builds described in building At the buffer area in area, wherein buffer area spacing is greater than the spatial resolution of remote sensing vegetation index;
S04: many years for calculating city and/or group of cities built-up areas from regional scale are averaged the more of vegetation index and buffer area Annual vegetation index;
S05: from regional scale calculate city and/or group of cities build up the average vegetation index of region variation tendency and The variation tendency of the average vegetation index in buffer zone;
S06: from grid cell size by calculated by pixel city and/or group of cities built-up areas vegetation index variation tendency and The vegetation index variation tendency of buffer area;
S07: the vegetation index significant changes area ratio for calculating city and/or group of cities built-up areas from grid cell size is gentle The vegetation index significant changes area ratio in area is rushed, the calculation method of the vegetation index significant changes area ratio is: calculated The pixel number that significant changes occur for vegetation index in same area accounts for the ratio of all pixel numbers;
S08: establishing many years is averaged vegetation index, vegetation index variation tendency, vegetation index significant changes area ratio Three indexs of example, along the dynamic changing curve of period, are asked in city and/or group of cities built-up areas and buffer area by curve matching It leads or visually judges to influence effective distance.
In a preferred embodiment, in S01, the remote sensing vegetation index is one or both of NDVI, EVI.
In a preferred embodiment, in S02, the remotely-sensed data is nighttime light data, remote Sensing Interpretation soil benefit With one or both of data.
In a preferred embodiment, institute in the flat mean of mean vegetation index variation tendency in region described in S05 and S06 Vegetation index variation tendency is stated using one in one-variable linear regression trend, F inspection, Sen+Mann-Kendall non-parametric test Kind or a variety of draftings.
In a preferred embodiment, turned using subset extraction, image mosaic, cut data, format conversion, projection It changes, the mode of quality inspection handles remote sensing vegetation index NDVI, EVI.
In a preferred embodiment, above-mentioned nighttime light data is selected from DMSP NTL data, NPP-VIIRS night lamp One or both of light remotely-sensed data.
In a preferred embodiment, above-mentioned DMSP NTL data are revised DMSP NTL data, described to correct Method include: mutual calibration, synthesis and the calibration of year border sequence in year.
In a preferred embodiment, above-mentioned one-variable linear regression trend is NDVI one-variable linear regression trend.
In a preferred embodiment, above-mentioned (1) is the average vegetation index in region described in S05 when need to draw When variation tendency, the calculation formula of the NDVI one-variable linear regression trend are as follows:
In formula, Slope indicates that research period region is averaged variation tendency, that is, Annual variations matched curve slope value of NDVI;
N is year;
I is time serial number;
xiFor the average Growing season NDVI value in 1 year region.
(2) when need to draw is vegetation index variation tendency described in S06, the NDVI one-variable linear regression trend Calculation formula are as follows:
In formula, Slope indicates the research period by the variation tendency of pixel NDVI;
N is year;
I is time serial number;
xI, jkIt is the year maximum NDVI value of jth row kth column pixel on 1 year NVDI image.
It is to be noted that needing to comprehensively consider institute in the building process of the buffer area of city and/or group of cities built-up areas It selects the spatial resolution of remotely-sensed data and influences the required precision of effective distance, the spacing of buffer area should be greater than remotely-sensed data sky Between resolution ratio, to guarantee that different buffer areas include different vegetation index pixels.
Compared with prior art, it has the following beneficial effects: according to the present invention
(1) a kind of urbanization process provided by the invention is applicable in the quantification detection method of Vegetation Effect effective distance In single city or Region urbanization's identification urban construction to the effective distance of Vegetation Effect, can be realized urban construction to plant It is affected the quantification detection of effective distance, has the characteristics that easy to use, robustness is good, with high accuracy.
(2) present invention by using long-term sequence data and for many years be averaged vegetation index, vegetation index variation tendency and Three indexs of vegetation index significant changes area ratio, can easy, intuitively detect city and/or group of cities urbanization into The activity such as urban sprawl measures the effective distance of Vegetation Effect with 36 cities and group of cities in following embodiments the most in journey Object is obtained as drawn a conclusion: 36 cities and group of cities built-up areas and the variation slope difference of buffer area vegetation index are obvious;36 Spatially there is notable difference, vegetation refers to coupling relationship trend between a city and group of cities built-up areas and each buffer area The ratio that the pixel of number significant changes accounts for whole pixels changes fairly obvious and regular between built-up areas and each buffer area It is relatively strong;With the continuous expansion of buffer area distance, built-up areas vegetation index is in first to increase the variation tendency to tend to be steady afterwards, Amplitude of variation significantly reduces after the buffer area 30-40km;It is slow that vegetation index change rate then becomes 0-10km from the negative value of built-up areas The positive value in area is rushed, and is gradually expanded, until being held essentially constant after the buffer area 30-40km;Vegetation index significant changes pixel institute What the variation of accounting example showed to dramatically increase obviously increases, the pixel ratio substantially reduced as ratio is increased along buffer area distance Example then becomes remote with buffer area distance and is obviously reduced, and variation reduces or tends towards stability after the buffer area 30-40km.Cause This, which can be the city ecological environment protection, urban landscaping, restoration of the ecosystem, ecological monitoring and assessment, ecology The work such as supervision determine that bounds, engineering construction point etc. provide direct technology support, can produce important social economy's effect Benefit.
Definition or paraphrase
NDVI:Normalized Difference Vegetation Index, normalized differential vegetation index, standard difference are planted By index, calculation formula are as follows:Wherein, ρNIRAnd ρREDRespectively represent near infrared band and feux rouges wave The reflectivity of section, the value of NDVI is between -1 and 1.
EVI:Enhanced Vegetation Index, enhancement mode meta file, calculation formula are as follows:Wherein, ρNIR、ρREDAnd ρBLUERespectively near infrared band, feux rouges wave The reflectivity of section and blue wave band.
The spatial resolution of remote sensing vegetation index: refer to the most narrow spacing for the two adjacent atural objects that can be identified on remote sensing image From the size or size of the minimum unit that can be distinguished in detail on remote sensing image.
The variation tendency of the average vegetation index in region: the average of all pixel vegetation indexs is used as area in completed region of the city The trend that increases or decreases of the domain average value by index, in calculation interval.
By pixel: all pixels in traversal region.
Robustness: robustness, insensitivity of the characterization control system to characteristic or parameter perturbation.
Detailed description of the invention
Fig. 1 is the process of the quantification detection method of the urbanization vegetation effect effective distance of embodiment according to the present invention Figure.
Fig. 2 is that the Chinese Growing season vegetation of the nineteen eighty-two of embodiment, 1992,2002 and 2013 refers to according to the present invention Number NDVI spatial framework.
Fig. 3 is 1992 and 2013 Chinese night remote sensing light datas of embodiment according to the present invention.
Fig. 4 is 36 main cities of China and group of cities built-up areas and 10 buffer areas of embodiment according to the present invention.
Fig. 5 is Chinese main cities and the variation of group of cities 1982-2013 vegetation index of embodiment according to the present invention Trend.
Fig. 6 be embodiment according to the present invention Chinese main cities and group of cities built-up areas and buffer area many years it is average Vegetation index.
Fig. 7 is the Chinese main cities of embodiment according to the present invention and the vegetation index of group of cities built-up areas and buffer area Variation tendency.
Fig. 8 be embodiment according to the present invention Chinese main cities and group of cities built-up areas and buffer area vegetation index it is aobvious Write variation pixel scale.
Specific embodiment
With reference to the accompanying drawing, specific embodiments of the present invention will be described in detail, it is to be understood that guarantor of the invention Shield range is not limited by the specific implementation.
Survey region:
Select GDP in 2015 be more than 500,000,000,000 yuan 34 cities and other 12 provincial capitals, based on totally 46 cities Study city, wherein the Yangtze River Delta, Pearl River Delta group of cities contain 12 cities altogether, therefore, analyze in total 36 cities and Group of cities.
Note: above-mentioned 36 cities and group of cities include: Harbin City, Urumqi City, Changchun, Shenyang City, exhale with it is great Special city, Beijing, Tianjin, Tangshan City, Daliang City, Yinchuan City, Shijiazhuang City, Taiyuan City, Yantai City, Weifang City, Jinan City, Xining, Qingdao City, Lanzhou, Zhengzhou City, Xi'an, Xuzhou City, Hefei City, Chongqing City, Wuhan City, Chengdu, Lhasa, Nanchang City, Changsha, Guiyang, Kunming, Fuzhou City, Quanzhou City, Nanning City, Haikou City and Pearl River Delta group of cities and long three Angle group of cities.
Choose data:
For a wide range of group of cities such as the whole world, each continent, the whole nation or megapolis, optional AVHRR (The Advanced Very High Resolution Radiometer, very high resolution radiometer), GIMMM (Global Inventory Modeling and Mapping Studies, the whole world detection with model study group), MODIS (Moderate Resolution Imaging Spectroradiometer, Moderate Imaging Spectroradiomete), SPOT (Systeme Probatoired ' Observation dela Terre, earth observation satellite system) etc. with continuous time series satellite remote sensing date, extract Vegetation index data;For single megalopolis, optional MODIS, Landsat (land satellite, the land of U.S. NASA Satellite) etc. image datas, extract vegetation index data.
Embodiment
In conjunction with attached drawing 1, the quantification detection method of urbanization vegetation effect effective distance is described in detail, it is specific to walk It is rapid as follows:
S01: the data set of many years space and time continuous remote sensing vegetation index of city and group of cities is established
It is specific: what the 15d maximum of selection NASA Ge Dade space center global monitoring and the production of analog study group was combined to The AVHRR GIMMMS NDVI of 8km3g(3g: referring to third generation AVHRR GIMMS data set) data set as vegetation index data, Time span is 1982-2013, wherein NDVI3gData are by subset extraction, image mosaic, cut data, format conversion, throwing The preprocessing process such as shadow conversion and quality inspection;The moon Value Data collection that MVC method obtains vegetation index is synthesized by maximum value, it is raw The NDVI composite value of the long season 4-10 month each monthly average characterizes annual vegetation growth, with the vegetative coverage situation of reflecting regional;
Gained nineteen eighty-two, 1992,2002 and 2013, China's Growing season vegetation index NDVI spatial framework was referring to attached Fig. 2.2 it is found that the comparison between the Growing season NDVI of nineteen eighty-two, 1992,2002 and 2013 shows that vegetation refers to reference to the accompanying drawings Number changes obviously, for example, being located at Ordos City south, the Mu Us Shadi vegetative coverage in Yulin City the north restores trend and shows It writes.Meanwhile also illustrate NDVI data can accurately reflect China's Macroscopic scale land surface vegetation growth conditions and its Spatial framework is that vegetation productivity and the effective of vegetative coverage act on behalf of one of index.
S02: the newest range in city and the built-up areas of group of cities in recent years is extracted based on remotely-sensed data
Specific: selection is using revised DMSP (Defense Meteorological Satellite Program, beauty State's Defence Meteorological Satellite Project) NTL (night time light, night steady light data) remote sensing nighttime light data, is obtained Take above-mentioned Urban Datas in 2013 and built-up areas spatial dimension;Wherein, DMSP is completed according to the method for Elvidge etc. and Liu et al. NTL data correct work, specifically include mutually calibration, synthesis and the calibration of year border sequence in year;
Chinese night remote sensing light data is referring to attached drawing 3 within gained 1992 and 2013.3 it is found that in China with reference to the accompanying drawings Eastern cityization area and western main cities night lights brightness value are larger, form striking contrast, energy with surrounding area Enough built-up areas spatial dimensions for extracting selected city.More phase comparisons also indicate that night remote sensing light data is able to reflect cities and towns and builds At the spatial expansion process in area, the especially megalopolis of the central and east, group of cities.
S03: the buffer area in building city and group of cities built-up areas
Specific: the NDVI data spatial resolution of use is about 8km, and using 10km as buffer area spacing, totally 10 are delayed Rush area, i.e. 100km other than outermost to completed region of the city outer boundary, and reject the water body in buffer area, other cities are built up The interference regions such as area;
36 cities of gained and the buffer area of group of cities are referring to attached drawing 4.4 it is found that 36 cities and group of cities with reference to the accompanying drawings And its buffer area is distributed in China four corners of the world everywhere, wherein central and east urbanization process is very fast, horizontal higher regional city Distribution is also more, and buffer area area is also larger, has stronger representativeness.
S04: calculating city and the built-up areas of group of cities from regional scale and many years of buffer area are averaged vegetation index
Firstly, obtaining 1982-2013 year-by-year using each city and group of cities built-up areas and buffer area vector boundary The average Growing season vegetation index in region;Then, the long-time average annual value of built-up areas, buffer area NDVI is calculated separately;
The average Growing season vegetation index ginseng in the region in the built-up areas 1982-2013 of gained city and group of cities each year It is shown in Table 1-1 to table 1-3, also there is similar tables of data in each buffer area.
The many years of the built-up areas and buffer area of city and group of cities are averaged vegetation index referring to table 2.As shown in Table 2, same Bu Tong annual region is averaged city and group of cities built-up areas, and vegetation index difference is obvious, and built-up areas and 10 buffer areas are mutual Between for many years be averaged vegetation index difference it is obvious.
Each city table 1-1 1982-1992 and group of cities build up the average Growing season vegetation index of region
Each city table 1-2 1993-202 and group of cities build up the average Growing season vegetation index of region
Each city table 1-3 2003-2013 and group of cities build up the average Growing season vegetation index of region
Each city of table 2 and group of cities built-up areas average production many years, vegetation index season
S05: the built-up areas in city and group of cities and the average vegetation index variation tendency of buffer area are calculated from regional scale
Vegetation index variation tendency is calculated using one-variable linear regression trend and the F method of inspection, wherein linear regression slope For NDVI variable quantity, it is used to examine the conspicuousness of this kind of variation tendency with the correlation in time;According to Principle of Statistics and generally acknowledge Convention, according to significance test as a result, variation tendency is divided into 2 grades: significant (P < 0.05) and not significant (P >=0.05);
When carrying out linear fit analysis using the NDVI numerical value changed over time, slope be can reflect out in the period Coupling relationship trend.Wherein, the calculation formula of NDVI one-variable linear regression trend are as follows:
In formula, Slope indicates between 1982-2013 that region is averaged variation tendency (the i.e. Annual variations matched curve of NDVI Slope value);
N is research period year, is 32, indicates 1982-2013 year sequence length;
I is 1-32, indicates 1982-2013 time serial number;
xiFor the average Growing season NDVI value in 1 year region.
The region of the built-up areas and buffer area of the city and group of cities vegetation index variation tendency that is averaged the results are shown in Table 3.By table 3 As it can be seen that city and group of cities built-up areas and buffer zone are averaged, the variation slope difference of vegetation index is obvious.
3 city 1982-2013 of table and group of cities build up region and are averaged the variation tendency (10 of vegetation index-4/ year)
S06: the built-up areas in city and group of cities and the vegetation index variation tendency of buffer area are calculated by pixel
In grid cell size, i.e., NDVI variation tendency is calculated using one-variable linear regression trend and the F method of inspection by pixel;
The built-up areas and buffer area of city and group of cities use one-variable linear regression trend by the vegetation index variation of pixel, Calculation formula is as follows:
In formula, by the variation tendency of pixel NDVI between Slope expression 1982-2013;
N is research period year, is 32, indicates 1982-2013 year sequence length;
I is 1-32, indicates 1982-2013 time serial number;
xI, jkIt is the year maximum NDVI value of jth row kth column pixel on 1 year NVDI image.
The result that the city 1982-2013 and group of cities built-up areas and buffer area are calculated by pixel vegetation index variation tendency Referring to attached drawing 5.5 it is found that coupling relationship trend is in space between city and group of cities built-up areas and each buffer area with reference to the accompanying drawings On there is notable differences.
S07: the built-up areas in city and group of cities and the vegetation index significant changes area ratio of buffer area are calculated
On grid cell size, dramatically increases, substantially reduces, increases and (wrap in built-up areas, each buffer area statistics NDVI respectively Include and dramatically increase and do not dramatically increase two parts) pixel scale;
National scale, Changjiang Delta urban agglomeration and Pearl River Delta group of cities built-up areas and each buffer area vegetation index significant changes Pixel occupied area ratio, referring to table 4.As shown in Table 4, either key cities such as national scale or the Yangtze River Delta, Pearl River Delta Group, it is clearly demarcated that the ratio that the pixel of vegetation index significant changes accounts for whole pixels changes ten between built-up areas and each buffer area It is aobvious, and regularity is stronger.
4 national scale of table, Changjiang Delta urban agglomeration and Pearl River Delta group of cities vegetation index are in the pixel institute of different variation tendencies Accounting example (%)
S08: establishing change curve, influences effective distance by curve matching derivation or visually judgement
Be averaged for many years three vegetation index, vegetation index variation tendency, significant changes area ratio indexs are established in city Built-up areas, multiple buffering area change curve, by visual observation i.e. can determine whether above-mentioned city (group) urbanization process to Vegetation Effect Effective distance be 30-40km.
National scale and each city and group of cities many years averagely vegetation index and 1982-2013 vegetation index change rate Variation along 10 buffer areas is shown in Table 5.National scale averagely vegetation index, 1982-2013 vegetation index change rate, plant for many years Attached drawing 6, attached drawing 7 and attached are shown in variation by index significant changes pixel occupied area ratio along built-up areas, buffer area distance respectively Fig. 8.
By table 5, attached drawing 6, attached drawing 7 and attached drawing 8 it is found that with buffer area distance continuous expansion, built-up areas are average for many years Vegetation index is in the variation tendency to tend to be steady afterwards is first increased, and amplitude of variation significantly reduces after the buffer area 30-40km; 1982-2013 vegetation index change rate then becomes the positive value of the buffer area 0-10km from the negative value of built-up areas, and is gradually expanded, until It is held essentially constant after the buffer area 30-40km;The variation of vegetation index significant changes pixel proportion shows to dramatically increase As ratio along buffer area distance increase and obviously increase, the pixel scale substantially reduced then with buffer area distance become it is remote and obvious Reduce, and amplitude of variation reduces or tends towards stability after the buffer area 30-40km.Vegetation index is (including aobvious in increase trend Write and increase and do not dramatically increase two parts) pixel proportion be also in the trend that increases far from built-up areas, and also in 30- It tends towards stability after the buffer area 40km, also demonstrates the above results.
Average NDVI are with 1982-2013 NDVI change rate along the variation of built-up areas and 10 buffer areas within table more than 5 years
The aforementioned description to specific exemplary embodiment of the invention is in order to illustrate and illustration purpose.These descriptions It is not wishing to limit the invention to disclosed precise forms, and it will be apparent that according to the above instruction, can much be changed And variation.The purpose of selecting and describing the exemplary embodiment is that explaining specific principle of the invention and its actually answering With so that those skilled in the art can be realized and utilize a variety of different exemplary implementation schemes of the invention and Various chooses and changes.The scope of the present invention is intended to be limited by claims and its equivalents.

Claims (9)

1. a kind of quantification detection method of urbanization vegetation effect effective distance, which is characterized in that the quantification monitoring side Method is based on long-term sequence remote sensing of vegetation data, comprising the following steps:
S01: many years space and time continuous remote sensing vegetation index of city and/or group of cities is established according to Remote Sensing Products or remote sensing image Data set;
S02: the newest range in built-up areas of city and/or group of cities is extracted based on remotely-sensed data;
S03: the spatial resolution based on remote sensing vegetation index sets the buffer area spacing of the built-up areas, constructs the built-up areas Buffer area, wherein buffer area spacing be greater than remote sensing vegetation index spatial resolution;
S04: be averaged many years of vegetation index and buffer area many years for calculating city and/or group of cities built-up areas from regional scale put down Equal vegetation index;
S05: city is calculated from regional scale and/or group of cities builds up the variation tendency and buffering of the average vegetation index of region The variation tendency of the average vegetation index of region;
S06: pass through the vegetation index variation tendency and buffering by pixel calculating city and/or group of cities built-up areas from grid cell size The vegetation index variation tendency in area;
S07: vegetation index significant changes area ratio and the buffer area of city and/or group of cities built-up areas are calculated from grid cell size Vegetation index significant changes area ratio, the calculation method of the vegetation index significant changes area ratio is: calculate it is same The pixel number that significant changes occur for vegetation index in area accounts for the ratio of all pixel numbers;
S08: establishing many years is averaged vegetation index, vegetation index variation tendency, vegetation index significant changes area ratio three A index in city and/or group of cities built-up areas and buffer area along the dynamic changing curve of period, by curve matching derivation or Visually judgement influences effective distance.
2. quantification detection method according to claim 1, which is characterized in that in S01, the remote sensing vegetation index is One or both of NDVI, EVI.
3. quantification detection method according to claim 1, which is characterized in that in S02, the remotely-sensed data is night lamp One or both of light data, remote Sensing Interpretation land use data.
4. quantification detection method according to claim 1, which is characterized in that the average vegetation in region described in S05 refers to Vegetation index variation tendency described in variation tendency and S06 is counted using one-variable linear regression trend, F inspection, Sen+Mann- One of Kendall non-parametric test or a variety of draftings.
5. quantification detection method according to claim 2, which is characterized in that use subset extraction, image mosaic, cutting Data, format conversion, projection transform, quality inspection mode handle remote sensing vegetation index NDVI, EVI.
6. quantification detection method according to claim 3, which is characterized in that the nighttime light data is selected from DMSP One or both of NTL data, NPP-VIIRS night lights remotely-sensed data.
7. quantification detection method according to claim 6, which is characterized in that the DMSP NTL data are revised DMSP NTL data, the method corrected include: mutual calibration, synthesis and the calibration of year border sequence in year.
8. quantification detection method according to claim 4, which is characterized in that one-variable linear regression trend is NDVI unitary Linear regression trend.
9. quantification detection method according to claim 8, which is characterized in that
(1) when need to draw is the flat mean of mean vegetation index variation tendency in region described in S05, the NDVI unitary line The calculation formula of property regressive trend are as follows:
In formula, Slope indicates that region between each year is averaged the variation tendency i.e. Annual variations matched curve slope value of NDVI;
N is year;
I is time serial number;
xiFor the average Growing season NDVI value in 1 year region.
(2) when need to draw is vegetation index variation tendency described in S06, the meter of the NDVI one-variable linear regression trend Calculate formula are as follows:
In formula, Slope indicates the variation tendency between each year by pixel NDVI;
N is year;
I is time serial number;
xI, jkIt is the year maximum NDVI value of jth row kth column pixel on 1 year NVDI image.
CN201910587655.6A 2019-07-01 2019-07-01 The quantification detection method of urbanization vegetation effect effective distance Pending CN110378576A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910587655.6A CN110378576A (en) 2019-07-01 2019-07-01 The quantification detection method of urbanization vegetation effect effective distance

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910587655.6A CN110378576A (en) 2019-07-01 2019-07-01 The quantification detection method of urbanization vegetation effect effective distance

Publications (1)

Publication Number Publication Date
CN110378576A true CN110378576A (en) 2019-10-25

Family

ID=68251506

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910587655.6A Pending CN110378576A (en) 2019-07-01 2019-07-01 The quantification detection method of urbanization vegetation effect effective distance

Country Status (1)

Country Link
CN (1) CN110378576A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111210166A (en) * 2020-02-17 2020-05-29 电子科技大学 Robustness assessment method for urban functional system
CN111402169A (en) * 2020-03-23 2020-07-10 宁波大学 Method for repairing remote sensing vegetation index time sequence under influence of coastal tide
CN111982822A (en) * 2020-09-28 2020-11-24 武汉工程大学 Long-time sequence high-precision vegetation index improvement algorithm
CN112116242A (en) * 2020-09-17 2020-12-22 福州福大经纬信息科技有限公司 Bare soil change identification method combining multiple remote sensing indexes
CN112561722A (en) * 2020-12-24 2021-03-26 滨州学院 Ecological system attribute component composition structure time evolution quantitative analysis method
CN112818923A (en) * 2021-02-25 2021-05-18 中国科学院地理科学与资源研究所 Urban mass living space construction time identification method
CN116011879A (en) * 2023-02-01 2023-04-25 长江水利委员会长江科学院 Ecological system stability assessment method and device, electronic equipment and storage medium
CN116596326A (en) * 2023-04-11 2023-08-15 常州双炬智能科技有限公司 Urban environment detection and comprehensive evaluation method based on remote sensing data
CN116957622A (en) * 2023-07-06 2023-10-27 成都理工大学 Urban mass urban economic development characteristic change analysis method combining noctilucent remote sensing
CN116596326B (en) * 2023-04-11 2024-04-26 泰州城发数字科技有限公司 Urban environment detection and comprehensive evaluation method based on remote sensing data

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103778241A (en) * 2014-02-10 2014-05-07 中国科学院南京地理与湖泊研究所 Method for identifying large-scale vegetation degeneration area by remote sensing
CN107480818A (en) * 2017-08-09 2017-12-15 中国热带农业科学院科技信息研究所 A kind of method that rapid evaluation human activities of vegetation covering change influences
WO2018081043A1 (en) * 2016-10-24 2018-05-03 Board Of Trustees Of Michigan State University Methods for mapping temporal and spatial stability and sustainability of a cropping system

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103778241A (en) * 2014-02-10 2014-05-07 中国科学院南京地理与湖泊研究所 Method for identifying large-scale vegetation degeneration area by remote sensing
WO2018081043A1 (en) * 2016-10-24 2018-05-03 Board Of Trustees Of Michigan State University Methods for mapping temporal and spatial stability and sustainability of a cropping system
CN107480818A (en) * 2017-08-09 2017-12-15 中国热带农业科学院科技信息研究所 A kind of method that rapid evaluation human activities of vegetation covering change influences

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
HARINI NAGENDRA,SUPARSH NAGENDRAN,SOMAJITA PAUL,SAJID PAREETH: "Graying, greening and fragmentation in the rapidly expanding Indian city of Bangalore", 《LANDSCAPE AND URBAN PLANNING》 *
杜加强,贾尔恒·阿哈提,赵晨曦,方广玲,阴俊齐,香宝,袁新杰,房世峰: "1982—2012 年新疆植被NDVI 的动态变化及其对气候变化和人类活动的响应", 《应用生态学报》 *

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111210166A (en) * 2020-02-17 2020-05-29 电子科技大学 Robustness assessment method for urban functional system
CN111210166B (en) * 2020-02-17 2023-06-20 电子科技大学 Robustness assessment method of urban functional system
CN111402169A (en) * 2020-03-23 2020-07-10 宁波大学 Method for repairing remote sensing vegetation index time sequence under influence of coastal tide
CN111402169B (en) * 2020-03-23 2023-04-11 宁波大学 Method for repairing remote sensing vegetation index time sequence under influence of coastal tide
CN112116242B (en) * 2020-09-17 2022-08-16 福州福大经纬信息科技有限公司 Bare soil change identification method combining multiple remote sensing indexes
CN112116242A (en) * 2020-09-17 2020-12-22 福州福大经纬信息科技有限公司 Bare soil change identification method combining multiple remote sensing indexes
CN111982822B (en) * 2020-09-28 2022-10-18 武汉工程大学 Long-time sequence high-precision vegetation index improvement algorithm
CN111982822A (en) * 2020-09-28 2020-11-24 武汉工程大学 Long-time sequence high-precision vegetation index improvement algorithm
CN112561722A (en) * 2020-12-24 2021-03-26 滨州学院 Ecological system attribute component composition structure time evolution quantitative analysis method
CN112818923A (en) * 2021-02-25 2021-05-18 中国科学院地理科学与资源研究所 Urban mass living space construction time identification method
CN116011879A (en) * 2023-02-01 2023-04-25 长江水利委员会长江科学院 Ecological system stability assessment method and device, electronic equipment and storage medium
CN116596326A (en) * 2023-04-11 2023-08-15 常州双炬智能科技有限公司 Urban environment detection and comprehensive evaluation method based on remote sensing data
CN116596326B (en) * 2023-04-11 2024-04-26 泰州城发数字科技有限公司 Urban environment detection and comprehensive evaluation method based on remote sensing data
CN116957622A (en) * 2023-07-06 2023-10-27 成都理工大学 Urban mass urban economic development characteristic change analysis method combining noctilucent remote sensing

Similar Documents

Publication Publication Date Title
CN110378576A (en) The quantification detection method of urbanization vegetation effect effective distance
WO2021184550A1 (en) Target soil property content prediction method based on soil transfer function
CN106909722B (en) A kind of accurate inversion method of large area of temperature near the ground
Yang et al. Remote sensing monitoring of grassland vegetation growth in the Beijing–Tianjin sandstorm source project area from 2000 to 2010
Chen et al. A data-model fusion approach for upscaling gross ecosystem productivity to the landscape scale based on remote sensing and flux footprint modelling
CN103513290B (en) Based on the region terrestrial ecosystems monitoring of respiration method of remote sensing
CN107145872A (en) Desert Riparian Forest spatial distribution acquisition methods based on GIS buffer zone analysis
CN108549858B (en) Quantitative evaluation method for urban heat island effect
CN104657935B (en) A kind of temperature inversion method near the ground
Wang et al. GIS and RS based assessment of cultivated land quality of Shandong Province
CN102289565A (en) Technical method for dynamically monitoring carbon reserve of forest ecological system
Asam et al. Estimation of grassland use intensities based on high spatial resolution LAI time series
CN109033543A (en) A kind of heterogeneous area&#39;s vegetation fraction estimation method, device and equipment of earth&#39;s surface
CN103455856B (en) A kind of technical method of city space identification of function
CN115204691B (en) Urban artificial heat emission estimation method based on machine learning and remote sensing technology
Qing-Ling et al. Topographical effects of climate data and their impacts on the estimation of net primary productivity in complex terrain: A case study in Wuling mountainous area, China
Wu et al. Evaluation of winter wheat yield simulation based on assimilating LAI retrieved from networked optical and SAR remotely sensed images into the WOFOST model
Gong et al. Evaluating the monthly and interannual variation of net primary production in response to climate in Wuhan during 2001 to 2010
Zhang et al. Impact of urban expansion on forest carbon sequestration: A study in Northeastern China.
Wang et al. Modeling the climatic effects of the land use/cover change in eastern China
CN107203679B (en) Method for evaluating influence of high-rise building shading on green land photosynthetic carbon sequestration capacity
Geng et al. Estimation of NPP in Xuzhou based on improved CASA model and remote sensing data
CN113987778A (en) Water and soil loss analog value space-time weighting correction method based on field station
Xie et al. Spatio-temporal process of oasification in the middle-Heihe River basin during 1368–1949 AD, China
You Determining paddy field spatiotemporal distribution and temperature influence using remote sensing in Songnen Plain, Northeastern 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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20191025