AU2021101776A4 - Ecosystem Service Supply-demand Index Change Detection Method Oriented to The Natural Resource Management Field - Google Patents
Ecosystem Service Supply-demand Index Change Detection Method Oriented to The Natural Resource Management Field Download PDFInfo
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Abstract
The invention relates to an ecosystem service supply-demand index change
detection method oriented to the natural resource management field. Firstly, an
ecosystem service supply-demand index is constructed by quantifying the ecosystem
service supply and the ecosystem service demands. Then the state of the ecosystem
service supply-demand index is measured by constructing an ecosystem service
supply-demand index grading table. Finally, the state changes of the ecosystem
service supply-demand index are analyzed by using a change detection method. The
invention overcomes the problem that the human demands of ecosystem
management are ignored, and improves the scientificity and rationality of the
ecosystemmanagement.
1/3
FIGURE OF THE SPECIFICATION
GDP(taking
logarithm)
Population(taking
logarithm)
FConstructionld
[ o e- .. proportion
IinL
---- - -- -- - L
Ecosystem service Ecosystem service Ecosystem service
supply supply- demand index -demand
Ecosystem service supply-demand index Construct ecosystem service
state change analysis supply-demand index grading table
Fig. 1
Legend Le
0 Ms 110 22 0 55 10 2
Fig. 2
Description
1/3
GDP(taking logarithm)
Population(taking logarithm)
IinL FConstructionld
[ o e- .. proportion
---- - -- -- - L Ecosystem service Ecosystem service Ecosystem service supply supply- demand index -demand
Ecosystem service supply-demand index Construct ecosystem service state change analysis supply-demand index grading table
Fig. 1
Legend Le
0 Ms 110 22 0 55 10 2
Fig. 2
Ecosystem Service Supply-demand Index Change Detection Method
Oriented to The Natural Resource Management Field
The invention relates to an ecosystem service supply-demand index
change detection method oriented to the natural resource management field,
which integrates coupling analysis of the ecosystem service supply and the
ecosystem service demands, and belongs to the field of ecosystem
management.
Ecosystem management is a response to global ecological,
environmental and resource crises and also a holistic approach to natural
resource management. Since the second half of the 20th century, the
ecological crisis has posed a great threat to the development of human society
in the process of rapid development of the world economy. At the same time,
with the acceleration of global economic integration and environmental issues
internationalization, the research hot point of macro-ecology has shifted to how
to scientifically manage the Earth's ecosystem. However, it is a hot and difficult
point to be solved in the field of ecosystem management about how to access
the state and the changes of the ecosystem due to the fact that the ecosystem
is affected by many non-linear factors in natural ecosystems and
socio-economic systems.
At present, the ecosystem management field mainly accesses the state of
the ecosystem from the field of ecosystem service supply. Common methods
include an alternative market technology, a simulated market technology and an equivalent factor method. However, the alternative market technology assessment requires a lot of preliminary work although it is objective and credible; the simulated market technology is affected by many subjective factors and is low in credibility although it is widely used; and the equivalent factor method is simple and straightforward, and is relatively comprehensive in assessment, but its calculation results are relatively low in accuracy.
At the same time, the ecosystem is not only affected by natural factors,
but also depends on social systems. Without human beneficiaries, the
structure and the process of the ecosystem cannot form ecosystem service. At
the same time, the economic activities of stakeholders have created huge
demands for ecosystem services and led to changes in ecosystem services.
Ecosystem management cannot be achieved if only the supply of ecosystem
services is considered while the human demands for ecological services are
ignored. Existing methods for assessing the assessment of ecological services
require questionnaires and other methods, which are time-consuming and
laborious, and therefore, it is difficult to compare the supply-demands of
ecosystem services within a certain time and spatial scope. Moreover, a
coupling mechanism of ecosystem service supply and demands cannot be
revealed for analyzing and accessing the changes in the supply-demand state
of ecosystem services.
To solve the problem, the invention provides an ecosystem service
supply-demand index change detection method oriented to the natural
resource management field. Firstly, an ecosystem service supply-demand
index is constructed. Then an ecosystem service supply-demand index grading table is constructed and supply-demand types of ecosystem services are divided based on the table. Finally, the changes of types of supply-demand indexes, in different years, of ecosystem services are analyzed by change detection.
The technical problem of the invention is mainly solved by the following
technical method:
Step 1, constructing an ecosystem service supply-demand index:
extracting an improved equivalent factor based on multiple factor data to
obtain ecosystem service supply results; quantifying ecosystem service
demand by using population, GDP, and construction land proportion data; and
constructing the ecosystem service supply-demand index according to formula
III, thereby realizing ecosystem service supply-demand coupling;
n ~Formula I ESP = Di * Li
Define ESP as the supply of ecosystem services, where Di is the area of
land use data, and Li is the improved equivalent factor of the land use type.
ESD=Axlg(B)xlg(C) Formula II
Define ESD as the demands for ecosystem services, where A is the
construction land proportion, B is the population density, and C is the GDP
density.
Formula III IESSD= ESP ESD
Define IESSD as the ecosystem service supply-demand index.
Step 2, constructing an ecosystem service supply-demand index grading
table: Constructing an ecosystem service supply-demand index grading table
according to the results of the national ecological civilization demonstration county, national garden city and national ecological environmental quality report, dividing the state of the ecosystem service supply-demand index into three categories including ecological deficit areas, ecological balance areas and ecological surplus areas, and five supply-demand states including surplus, relative surplus, balance, overload and severe overload.
Table 1 Ecosystem Service Supply-demand Index Grading Table
Types Supply-demand states IESSD Ecological deficit areas Severe overload IESSD<0.92 Overload 0.92 CIESSD<3.9 Ecological balance areas Balance 3.961ESSD<12.15 Ecological surplus areas Relative surplus 12.15 IESSD<50.6 Surplus IESSD>50.6
Step 3, using the change detection method to analyze the state changes
of the ecosystem service supply-demand index, where the row in Table below
represents the state area of the ecosystem service supply-demand index at
time T1, and the column represents the state area of the ecosystem service
supply-demand index at time T2; Pij represents the percentage of the area to
the total land area while the state i of the ecosystem service supply-demand
index is converted to the state j during the period of T1-T2; Pi. represents the
total area percentage of the state i at time Ti; P+j represents the total area
percentage of the state type of the ecosystem service supply-demand index of
the point j at time T2; Pi+-Pii represents area reduction percentage of the state i
at time T1-T2, P+j-Pji represents area increase percentage of the state j of the
ecosystem service supply-demand index at time T1-T2.
Table 2 State Change Analysis of Ecosystem Service
Supply-demand Index
T1 Ai A2 ... An Pi+ Reduced
Ai P1 1 P 12 ... Pln Pi+ P1+-P11 A2 P2 1 P2 2 ... P2n P2+ P2+-P22
An Pn1 Pn2 ... Pnn Pn+ Pn+-Pnn P.j P+1 P+2 ... P+n 1 Newly added P+1-P11 P+2-P22 P+n-Pnn
Therefore, the invention has the following advantages: firstly, an
ecosystem service supply-demand index is constructed by quantifying the
ecosystem service supply and the ecosystem service demands; then the state
of the ecosystem service supply-demand index is measured by constructing
an ecosystem service supply-demand index grading table; and finally, the
state changes of the ecosystem service supply-demand index are analyzed by
using a change detection method. The invention overcomes the problem that
the human demands of ecosystem management are ignored, and improves
the scientificity and rationality of the ecosystem management.
Fig. 1 is a model flow chart of the invention.
Fig. 2 is an ecosystem service supply diagram of Example 1.
Fig. 3is an ecosystem service demand diagram of Example 1. Fig. 4 is an ecosystem service supply-demandindexdiagram ofExample
1.
Fig. 5 is an ecosystem service supply-demand index change diagram of
Example 1.
The technical scheme of the invention will be further described in detail in
combination with accompanying drawings and specific examples.
Example:
The model flow chart adopted by the invention is as shown in Fig. 1.
The assessment of the state changes of the ecosystem service
supply-demand index includes the following steps:
step 1, constructing an ecosystem service supply-demand index:
constructing the ecosystem service supply-demand index by quantifying the
supply and demands of ecosystem services to realize coupling of ecosystem
service supply and demands;
step 2, analyzing the state of the ecosystem service supply-demand
index: analyzing the state of the ecosystem service supply-demand index by
constructing an ecosystem service supply-demand index grading table; and
step 3, analyzing the changes in the state of the ecosystem service
supply-demand index: analyzing the state changes of the ecosystem service
supply-demand index by the change detection methods.
Provided is a specific example adopting the method.
1. Based on the improved equivalent factor, the ecosystem service supply
data in 2000 and 2015 were obtained, as shown in Fig. 2; the ecosystem
service demands in 2000 and 2015 were quantified by population, GDP, and
construction land proportion, as shown in Fig. 3; the ArcGIS10.4 field
calculator function was utilized to perform range standardization on supply and
demand data in 2000 and 2015; the ArcGIS10.4 field calculator is utilized to
create new IESSD field and couple ecosystem service supply and demand
data so as to construct the ecosystem service supply-demand index.
2. According to the results of the national ecological civilization
demonstration county, national garden city and national ecological
environmental quality report, the ArcGIS10.4 spatial analysis function is used
to construct the ecosystem service supply-demand index state grading table, and the ecosystem service supply-demand index in 2000 and 2015 is divided into five states including surplus, relative surplus, balance, overload and severe overload, as shown in Fig. 4.
3. The state changes of the ecosystem service supply-demand index from
2000 to 2015 are obtained by using the change detection method, as shown in
Fig. 5.
The specific examples described in the invention are merely illustrative of
the spirit of the invention. A person skilled in the art can make various
modifications or additions to the specific example described or in a similar
manner, without departing from the spirit of the invention or the scope as
defined by the appended claims.
Claims (1)
1. An ecosystem service supply-demand index change detection method
oriented to the natural resource management field, characterized by coupling
ecosystem service supply and demand to analyze state changes of the
ecosystem service supply-demand index, specifically comprising the following
steps:
step 1, constructing an ecosystem service supply-demand index:
extracting an improved equivalent factor based on multiple factor data to
obtain ecosystem service supply results; quantifying ecosystem service
demand by using population, GDP, and construction land proportion data; and
constructing the ecosystem service supply-demand index according to formula
III, thereby realizing ecosystem service supply-demand coupling;
n ~Formula I ESP = Di * Li
define ESP as the supply of ecosystem services, wherein Di is the area of
land use data, and Li is the improved equivalent factor of the land use type;
ESD=Axlg(B)xlg() Formula II
define ESD as the demands for ecosystem services, wherein A is the
construction land proportion, B is the population density, and C is the GDP
density;
Formula III IESSD= ESP ESD
define IESSD as the ecosystem service supply-demand index.
Table 1 Ecosystem Service Supply-demand Index Grading Table
Types Supply-demand states IESSD Severe overload IESSD<0.92 Ecological deficit areas Overload 0.926|ESSD<3.9 Ecological balance areas Balance 3.96IESSD<12.15 Ecological surplus areas Relative surplus 12.156IESSD<50.6 Surplus IESSD>50.6
Step 2, constructing anecosystem service supply-demand index grading
table: constructing an ecosystem service supply-demand index grading table
according to the results of the national ecological civilization demonstration
county, national garden city and national ecological environmental quality
report, dividing the state of the ecosystem service supply-demand index into
three categories including ecological deficit areas, ecological balance areas
and ecological surplus areas, and five supply-demand states including surplus,
relative surplus, balance, overload and severe overload;
Step 3, using the change detection method to analyze the state changes
of the ecosystem service supply-demand index, wherein the row in Table
below represents the state area of the ecosystem service supply-demand
index at time T1, and the column represents the state area of the ecosystem
service supply-demand index at time T2; Pij represents the percentage of the
area to the total land area while the state i of the ecosystem service
supply-demand index is converted to the state j during the period of T1-T2; Pi+
represents the total area percentage of the state i at time Ti; P+j represents the
total area percentage of the state type of the ecosystem service
supply-demand index of the point j at time T2; Pi+-Pii represents area reduction
percentage of the state i at time T1-T2, Pj-Pjj represents area increase percentage of the state j of the ecosystem service supply-demand index at time T1-T2.
Table 2 State Change Analysis of the Ecosystem Service Supply-demand
Index
T1 Ai A2 ... An Pi+ Reduced A1 P11 P12 ... Pin Pi+ Pi+-Pii A2 P21 P22 ... P2n P2+ P2+-P22
An Pni Pn2 ... Pnn Pn+ Pn+-Pnn P~j P+i P+2 .. P+n 1 Newly added P+i-Pii P+2-P22 P+n-Pnn
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