
- Journal of Geographical Sciences
- Vol. 30, Issue 7, 1043 (2020)
Abstract
There is an extremely complex coercive relationship between urbanization and the eco-environment. Coordinating the relationship between them is a global strategic issue. To address this scientific difficulty, since 2005, a series of international scientific organizations and research programs have carried out research on the topic. In 2005, the International Human Dimensions Program on Global Environmental Change (IHDP) formulated an “urbanization and global environmental change” research plan, which became its core area of work. It proposed strengthening research on the coupling relationship between urbanization and global environmental change using intersecting spatio-temporal scales, spatio-temporal scale comparisons and exchanges between public and policymakers (
1 Coupling characteristics, coupling intensity and the coupling tower
The mutual coupling process between urbanization and the eco-environment is a huge complex system involving social, economic, and natural elements. Scholars from various disciplines have proposed coupling analysis frameworks for this huge system (
1.1 Coupling characteristics
Coupling is a concept commonly used in physics, biology, systems science, and chemistry. It refers to the dynamic relationship between two or more systems with movements that are interdependent, coordinated and mutually promoting, as well as to the result of their ultimate development. Coupling is the internal working methods and operating rules and principles (or technical paths) used by two or more interdependent system elements to achieve a coordinated and mutually promoting dynamic relationship (high coordination is coupling) (
Figure 1.
Of these, the coupling constant is a critical parameter that indicates that recurrence between the two systems is in a highly cooperative state. Above or below this parameter, coupling between the two systems is broken and they enter a non- cooperative, uncoupled state. At certain time and space scales, the coupling constant is a constant quantity, but the coupling constant changes with changes in time and space in order to find a new coupling constant in the spatio-temporal scale. The coupling agent - also called the coupling medium - refers to media such as materials, energy and information in the exchange process that systems rely on to achieve a certain intensity of coupling. Without the transmission and exchange of material, energy or information between systems, the system is unable to complete the coupling process.
1.2 Coupling intensity
Coupling intensity is a measure of the degree of association and coordination between systems. The greater the connection between systems, the greater the intensity of coupling (indicating that the extent of the connection and of dependence between the systems is close), and the stronger the coupling characteristics. In fact, changes to mutual coercion and coupling between urbanization and the eco-environment are a nonlinear process (
where
where
Figure 2.
1.3 Coupling tower
Based on the intensity of coupling between the urbanization area and the eco-environment area, coupling can be divided into six types: random coupling, indirect coupling, loose coupling, cooperative coupling, close coupling and controlled coupling, which together make up a “coupling tower” between urbanization and the eco-environment (
Figure 3.
Coupling | Independence | Association | Strength of | Coupling | Coupling path | Position in |
---|---|---|---|---|---|---|
Random | Strongest | Very weak | Very low | 0-10 | Adaptive coupling | Lowest |
Indirect | Quite strong | Quite weak | Low | 10-30 | Adaptive organization | Low |
Loose | Moderate | Moderate | Medium | 30-50 | Adaptive regulation | Middle |
Cooperative | Quite weak | Quite high | High | 50-70 | Regulation | Upper-middle |
Close | Very weak | Very high | Very high | 70-90 | Regulation | High |
Controlled | Weakest | Highest | Full | 90-100 | Control | Highest |
Table 1.
Types of coupling and structure of the coupling tower
(1) Random coupling. Random coupling means that there is no relationship between the two major systems of urbanization and the eco- environment, or that the two major systems are independent of each other and do not interfere with each other. The two major systems can cooperate if they wish, or not, but it does not affect the normal function of the systems. Under random coupling, the urbanization system and the eco-environment system have the strongest independence, the lowest degree of coupling, and the weakest, or no correlation. The coupling path is usually an adaptive path, and the strength of coupling is very low. It is the lowest part of the coupling tower.
(2) Indirect coupling. Indirect coupling means that there is no direct relationship between the two systems of urbanization and the eco-environment, or the degree of mutual interference between the two systems is very low, and the degree of association between the two systems is low, with only an indirect relationship, rather than a direct relationship. The urbanization system and the eco-environment system are quite strongly independent, and the intensity of coupling is low, generally between 10% and 30%. The coupling path is usually an adaptive organizational path, and the strength of coupling is low. It has a low position in the coupling tower.
(3) Loose coupling. Loose coupling refers to when one of the two systems of urbanization and the eco-environment accesses another system, exchanges input/output information with each other through data parameters (not control parameters, public data structures or external variables). The loosely coupled urbanization system and the eco-environment system have moderate independence. There is a moderate intensity of coupling, generally between 30% and 50%. The coupling path is usually an adaptive control path, and the strength of coupling is moderate. It has a middle position in the coupling tower.
(4) Cooperative coupling. Cooperative coupling refers to when one of the two systems of urbanization and the eco-environment requires the cooperation of the other system to function normally. The urbanization and eco-environment systems have quite weak independence. The degree of association between them is quite high, and they have quite high coupling intensity, generally between 50% and 70%. The coupling path is usually a regulatory path, and the strength of coupling is high. It occupies an upper-middle position in the coupling tower.
(5) Close coupling. Close coupling refers to a high degree of dependence of one system in the two systems of urbanization and the eco-environment on the other system in order to function normally. The systems have very weak independence. The degree of association between them is quite high, and they have high coupling intensity, generally between 70% and 90%. The coupling path is usually a regulatory path, and the strength of coupling is very high. It occupies a high position in the coupling tower.
(6) Controlled coupling. Within the urbanization and eco-environment systems, controlled coupling is present if a change in the logical relationship of a control parameter within one system affects the normal operation of that system as well as of the other system. Independence of the urbanization system and the eco-environment system is the weakest under controlled coupling. The degree of association between the systems is the highest, and they have very high coupling intensity, generally between 90% and 100%. The coupling path is usually a regulatory path, and the strength of coupling is fully coupled. It sits at the top of the coupling tower.
2 Coupling circle theory and graphs
A complex mutually coercive relationship objectively exists between urbanization and the eco-environment. The future of theoretical research in this area and the question we are trying to answer is which technological path can be used to find the best coupling point of mutual coercion between urbanization and the eco-environment (
2.1 Urbanization and eco-environment coupling circle theory
The urbanization and eco-environment coupling circle theory is based on urbanization and eco-environment mutual coupling theory. It integrates three original areas into two areas, turns original external intervention and regulation into internal self-organization, and changes an original single-line graph into a multi-line graph to create a new theory and new graph. The basic viewpoints of the urbanization and eco-environment coupling circle theory are that a near-distance, nonlinear coupling relationship objectively exists between urbanization and the eco-environment; this nonlinear coupling relationship can be quantified in terms of coupling intensity, and a “coupling tower” can be created based on that intensity; urbanization and eco-environment coupling circles can have linear, exponential-curve, logarithmic-curve, double exponential-curve and S-curve coupling graphs, and the S-curve graph is considered the best graph as it embodies the optimal mutual coupling scenario; coupling circles can be regulated using a developed coupler so that the urbanization and eco-environment areas always remain in the most dynamic and orderly state; over time, the degree of coupling between urbanization and the eco-environment displays a wave-like ascending pattern, which is called the coupling climbing law or coupling ladder, whereby each instance of coupling will rise to a new height, promoting sustainable urban development, and each instance coercion will lead to a decline in sustainable urban development.
2.2 Theoretical graphs of urbanization and eco-environment coupling
In accordance with the urbanization and eco-environment coupling circle theory, to reflect the development stages and urbanization models of different cities, this study has created linear, exponential-curve, logarithmic-curve, double exponential-curve and S-curve coupling graphs of urbanization and eco-environment coupling circles. Each type of graph is divided into nine graphs (
Figure 4.
(1) Urbanization and eco-environment linear coupling graphs. Linear coupling graphs refer to graphs in which the coupling boundary between the urbanization area and the eco-environment area in the course of the evolution of the urbanization and eco-environment coupling circle is in the form of a linear function (
where
Figure 5.
(2) Urbanization and eco-environment exponential-curve coupling graphs. Exponential-curve coupling graphs refer to graphs in which the coupling boundary between the urbanization area and the eco-environment area in the course of the evolution of the urbanization and eco-environment coupling circle is in the form of an exponential function (
where
Figure 6.
(3) Urbanization and eco-environment logarithmic-curve coupling graphs. Logarithmic-curve coupling graphs refer to graphs in which the coupling boundary between the urbanization area and the eco-environment area in the course of the evolution of the urbanization and eco-environment coupling circle is in the form of a logarithmic function (
where
Figure 7.
(4) Urbanization and eco-environment double exponential-curve coupling graphs. Double exponential-curve coupling graphs refer to graphs in which the coupling boundary between the urbanization area and the eco-environment area in the course of the evolution of the urbanization and eco-environment coupling circle is in the form of a double exponential function (
where
Figure 8.
(5) Urbanization and eco-environment S-curve coupling graphs. S-curve coupling graphs refer to graphs in which the coupling boundary between the urbanization area and the eco-environment area in the course of the evolution of the urbanization and eco-environment coupling circle is in the form of an S-shaped function (
where
Figure 9.
3 Coupling circles and optimal regulation
A comparative analysis of the linear, exponential-curve, logarithmic-curve, double exponential-curve, and S-curve graphs reveals the following: the linear graph is an ideal graph for coupling urbanization with the eco-environment; the exponential-curve graph is the worst graph for coupling urbanization with the eco-environment; the logarithmic-curve graph is the inferior graph for coupling urbanization with the eco-environment; the double exponential-curve graph is the suboptimal graph for coupling urbanization with the eco-environment; and the S-curve graph is the optimal graph for coupling urbanization with the eco-environment (
Figure 10.
3.1 Coupler modules
By enlarging the optimal S-curve graph to the module level, we can discover the spatial structure of the S-curve graph. Using the S-curve as the coupling boundary, the left half is the urbanization area. It is composed of human elements, such as population, economy, society, and construction land. It is where the main human processes occur based on the laws of humanity (
Figure 11.
3.2 Coupler variables
If the optimal S-curve graph is enlarged further from the module level to the variable level, we discover that there are 201 variables that help regulate the S-curve graph (
Coupler module name | Number of coupler variables | Coupler variable names |
---|---|---|
Water | 41 | 12 water consumption indicators (total water demand, industrial water demand, domestic water demand, agricultural water demand, ecological water demand, total water supply, recycled water use, seawater desalination, allocated water resources, local water supply, local water resources, gap between supply and demand); 16 structural indicators of water use (rural domestic water demand, urban domestic water demand, livestock water demand, large livestock water demand, number of large livestock, small livestock water demand, number of small livestock, water demand for irrigation, irrigated area, forestry water demand, grassland water demand, fishery water demand, surface water supply, surface water resources, groundwater supply, groundwater resources); 13 quota/coefficient indicators (water consumption per 10,000 yuan industrial value added, per capita rural domestic water consumption, per capita urban domestic water consumption, large livestock water requirement quota, small livestock water requirement quota, effective irrigation coefficient, irrigation quota, forestry water requirement quota, pasture water requirement quota, fishery water requirement quota, recycled water rate, surface water extraction rate, groundwater extraction rate) |
Economy | 21 | 9 economic totals/structure indicators (GDP, value added of primary industry, value added of secondary industry, value added of tertiary industry, total retail sales of consumer goods, total fiscal revenue, total imports and exports, value added of industry, total fixed-asset investment); 6 economic averages/coefficient indicators (GDP per capita, contribution of scientific and technological progress to economic growth, impact of actual use of foreign capital, GDP conversion into fiscal income coefficient, economic openness, and proportion of industrial added value); 6 economic growth indicators (increment in primary industry, growth rate of primary industry, increment in secondary industry, growth rate of secondary industry, increment in tertiary industry, growth rate of tertiary industry) |
Society | 9 | 3 indicators of per capita income of residents (national per capita disposable income, urban per capita disposable income, rural per capita disposable income); 4 resident income growth indicators (urban per capita disposable income increment, urban per capita disposable income growth coefficient, rural per capita disposable income increment, rural per capita disposable income growth coefficient); 2 social development indicators (number of mobile phones, number of Internet users) |
Population | 23 | 5 population totals/structure indicators (total population, urban population, level of urbanization, rural population, population density); 10 population change indicators (population growth, migrant population, population migration rate, number of births, population birth rate, population reduction, emigration, emigration rate, number of deaths, mortality rate); 8 employment indicators (employed population, employment-to-population coefficient, population employed in primary industry, primary industry employment-to-population coefficient, population employed in secondary industry, secondary industry employment-to-population coefficient, population employed in tertiary industry, tertiary industry employment-to-population coefficient) |
Construction Land | 28 | 7 construction land indicators (urban and rural construction land area, urban construction land area, urban per capita construction land area, rural residential construction land area, rural per capita construction land area, transportation, industry, mining and other construction land area, highway mileage); 6 construction land change indicators (urban area increase, urban area decrease, rural residential area increase, rural residential area decrease, transportation, industry and mining area increase, transportation, industry and mining area decrease); 15 land type conversion indicators (urban area converted to forest, urban area converted to grassland, urban area converted to unused land, urban area converted to water area, urban area converted to cultivated land, rural settlement converted to forest area, rural settlement area converted to grassland, rural settlement area converted to unused land, rural residential area converted to water area, rural residential area converted to arable land, transportation, industry and mining area converted to forest, transportation, industry and mining area converted to grassland, transportation, industry and mining area converted to unused land, transportation, industry and mining area converted to water area, transportation, industry and mining area converted to arable land) |
Arable Land | 11 | 2 arable land/land indicators (arable land area, total land area); 2 arable land change indicators (arable land area increase, arable land area decrease); 7 land type conversion indicators (arable land to forest land area, arable land to grassland area, conversion of arable land to unused land area, conversion of cultivated land to water area, conversion of cultivated land to urban area, conversion of cultivated land to rural residential area, conversion of cultivated land to transportation, industry and mining area) |
Ecology | 38 | 13 ecological land/ecosystem service indicators (ecological land area, forest area, grassland area, unused land area, water area, forest land ecological service value, forest land ecological service value coefficient, grassland ecological service value coefficient, grassland ecological service value coefficient, unused land ecological service value, unused land ecological service value coefficient, water area ecological service value, water area ecological service value coefficient); 8 indicators of ecological land change (forest land area increase, forest land area decrease, grassland area increase, grassland area decrease, unused land area increase, unused land area decrease, water area increase, water area decrease); 17 land type conversion indicators (conversion of forest to urban area, conversion of forest to rural settlement area, conversion of forest to transportation, industry and mining land area, conversion of forest to arable land area, conversion of grassland to urban area, conversion of grassland to rural residential area, conversion of grassland to transportation, industry and mining area, conversion of grassland to arable land area, conversion of unused land to urban area, conversion of unused land to rural residential area, conversion of unused land to transport, industry and mining area, conversion of unprofitable land to arable land area, conversion of water to urban area, conversion of water to rural residential area, conversion of water to transportation, industry and mining area, conversion of water to arable land area) |
Pollution | 20 | 11 “three wastes”/environmental indicators (total waste water, industrial waste water discharge, domestic waste water discharge, industrial waste gas emission, solid waste generated, industrial solid waste generated, domestic waste generated, urban domestic waste generated, rural domestic waste generated, per capita domestic waste generated, PM2.5 concentration); 4 environmental treatment efficiency indicators (industrial wastewater treatment rate, domestic wastewater treatment rate, comprehensive industrial solid waste treatment volume, industrial solid waste synthesis treatment rate); 5 pollution emission intensity indicators (industrial wastewater discharge coefficient, exhaust gas emissions per 10,000 yuan of industrial value added, waste generated per 10,000 yuan of industrial value added, industrial SO2 emissions, industrial SO2 emissions ratio coefficient) |
Energy | 10 | 4 energy consumption indicators (energy consumption, industrial energy consumption, domestic energy consumption, total carbon emissions); 6 average energy consumption indicators (energy consumption per unit of industrial value added, energy consumption elasticity coefficient, per capita domestic energy consumption, energy consumption per capita, energy consumption per unit of GDP, carbon emissions per 10,000 yuan of GDP) |
9 | 201 | 201 |
Table 2.
Variables of the urbanization and eco-environment coupler
3.3 Coupler dynamic regulation
Dynamic regulation of urbanization and eco-environment coupling includes three major aspects: static regulation between multiple urbanization areas and eco-environment areas at the same time, dynamic regulation between the same urbanization area and eco-environment area at different times, and dynamic regulation between multiple urbanization areas and eco-environment areas at different times.
(1) Static coupling of multiple cities and multiple elements at the same time. This refers to the complex coupling relationships formed by multiple elements of multiple cities at the same time within an urban agglomeration. At different spatial scales at the same time within the agglomeration, this type of regulation is characterized by optimization of the allocation of various resources, environmental improvements, joint construction and sharing of inter-city infrastructure and public services, cooperation between multiple cities, and rational adjustments to multiple elements within multiple cities, to ultimately achieve static coupling within a fixed time. Over time, the multi-element static coupling is quickly broken, and in the new time period, it either evolves into a new static coupling state or leads to static imbalance, depending on the inter-annual optimization and rational allocation of multiple elements in the two time periods.
(2) Dynamic coupling of multiple cities and multiple elements at different times. This refers to the dynamic coupling relationships formed by multiple elements of multiple cities at different times within an urban agglomeration. At different spatial scales at different times within the urban agglomeration, this type of regulation is characterized by different cities in the agglomeration achieving intergenerational optimized allocation of resources, intergenerational improvements in regional eco-environments, intergenerational coordinated construction and sharing of infrastructure and public services between cities, cooperation between multiple cities, and rational adjustments to multiple elements within multiple cities, to ultimately achieve dynamic coupling of multiple cities at different times. As time passes, multi-element dynamic coupling is gradually optimized into a new dynamic coupling state, which will promote the evolution from low-level coupling to high-level coupling between urbanization and the eco-enviroment within the urban agglomeration.
(3) Dynamic coupling of a single city and multiple elements at different times. This refers to the dynamic coupling relationships formed by multiple elements of an urban agglomeration at different times, or by multiple elements of a specific city in an urban agglomeration at different times. At different spatial scales at different times within the urban agglomeration, this type of regulation is characterized by the agglomeration achieving intergenerational optimized allocation of resources, intergenerational improvements in regional eco-environments, intergenerational coordinated construction and sharing of infrastructure and public services between cities, cooperation between multiple cities, and rational adjustments to multiple elements within multiple cities, to ultimately achieve dynamic coupling at different times. As time passes, multi-element dynamic coupling is gradually optimized into a new dynamic coupling state, which will promote the evolution from low-level coupling to high-level coupling between urbanization and the eco-environment within the urban agglomeration.
4 Conclusions and discussion
(1) It has been objectively identified that there is an extremely complex near-distance coupling relationship between urbanization and the eco-environment. We have shown the coupling nature, coupling relationship, coupling intensity and coupling tower of interactions between urbanization and the eco-environment; summarized 10 relationships and interactions of urbanization and eco-environment coupling based on the main control elements; and divided coupling nature according to intensity into six types, namely, very low, low, medium, high, very high and full coupling, which correspond to the categories of random coupling, indirect coupling, loose coupling, cooperative coupling, close coupling, and controlled coupling, thereby forming a “coupling tower” of urbanization and the eco-environment.
(2) We created an urbanization and eco-environment coupling circle theory and graphs. A total of 45 linear, exponential-curve, logarithmic-curve, double exponential-curve and S-curve graphs were generated based on each 10° of rotation, with the different graphs corresponding to different urban development stages, models and characteristics. Of the various coupling graphs, the S-curve coupling graph is considered optimal, as it reflects the best coupling scenario of interactivity between urbanization and the eco-environment.
(3) We developed an urbanization and eco-environment coupler (UEC) for regulation and control. Using an enlarged S-curve coupling graph, and with the help of an SD model and based on the complex one-to-one, one-to-many, and many-to-many relationships between the variables, we developed the UEC, which is composed of 11 regulating elements and 201 variables, for regulation and control. The coupler includes three spatio-temporal scales: static regulation between multiple urbanization areas and eco-environment areas at the same time, dynamic regulation between the same urbanization area and eco-environment area at different times, and dynamic regulation between multiple urbanization areas and eco-environment areas at different times. The coupler ensures the urbanization and eco-environment areas maintain an optimal dynamic and orderly state. Any change in any of the variables changes the whole, affecting the structure, function and regulation of the entire coupler.
(4) Verifying the coupling theory and coupling regulation through applications is an important area of future research. Due to limitations in its scope, this article simply proposed the basic ideas, graphs and coupler for urbanization and eco-environment coupling circle theory. Using the Beijing-Tianjin-Hebei urban agglomeration as a case study for verification, we developed urbanization and eco-environment coupler software, the results of which are published in a separate study. Future studies could analyze other urban agglomerations in order to discover universal principles and draw further conclusions.
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