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Simulation of Urban Growth and Urban Living Environment with Release of the Green Belt

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Simulation of Urban Growth and Urban Living Environment with Release of the Green Belt sustainability Article Simulation of Urban Growth and Urban Living Environment with Release of the Green Belt Seongwoo Jeon 1 , Hyunjung Hong 1,2,* and Sungdae Kang 3 1 Department of Environmental Science and Ecological Engineering, Korea University, 145 Anam-ro, Seongbuk-gu, Seoul 02841, Korea; [email protected] 2 Korea Environment Institute, 370 Sicheong-daero, Sejong 30147, Korea 3 Green Simulation Co., Ltd., 1523 Jungang-daero, Dongrae-gu, Busan 47710, Korea; [email protected] * Correspondence: [email protected] or [email protected] Received: 29 June 2018; Accepted: 11 September 2018; Published: 12 September 2018 Abstract: Green belts in developing or developed countries have been released because city-center development has reached a saturation point, and the strict protections and restrictions within green belts has led to an increase in opposition from local residents and property owners. However, green belt release has led to urban growth within the associated regions and cities, resulting in an increase in the temperature and the accumulation of pollutants in the atmosphere. We intend to prove quantitatively the effect of the release of green belts at the local level based on the interactions among land cover, climate, and air quality and to provide information for policy decisions accordingly. Our simulation results show that the urban areas of Jeju and Chuncheon, in South Korea, where green belts have been completely released, will increase by up to 21.83% by 2025 and 123.93% by 2020, respectively, compared to areas that have retained green belts. The simulations also show that the surface temperature within the released region of Jeju and Chuncheon will increase by up to 0.83% by 2025 and 0.03% by 2020, respectively. The average atmospheric concentrations within the released region of Jeju and Chuncheon were modelled to increase by up to 256.93% by 2025 and 337.29% by 2020, respectively. Keywords: green belt; urban growth; land cover; urban living environment; climate change; surface temperature; air quality; atmospheric concentration; conservation; sustainable use 1. Introduction Rapid urban growth and land development following industrialization and urbanization have led to overpopulation, housing shortages, traffic jams, and damage to the environment [1]. To address these issues, the green belt system was introduced. However, green belts have been released, especially in developing or developed countries [2,3], because (1) development of the city centers has reached a saturation point and (2) the strict protection and development restrictions within green belts has led to an increase in opposition from local residents and property owners [4,5]. Developing or developed countries have been attempting to rationalize the change in the type of land use (land cover) by releasing green belts in locations with low conservation value, or where the purpose of the original designation has been achieved. Portions of green belts have been released, and such adjustments are expected to continue in the near future, based on applicable regional urban master planning. In combination with increasing demand and pressure for community development, land use changes rapidly with the release of green belts. Urban regions released from their green belts have spread in connection with existing downtowns. The expansion of urban regions that have been Sustainability 2018, 10, 3260; doi:10.3390/su10093260 www.mdpi.com/journal/sustainability Sustainability 2018, 10, 3260 2 of 21 released from green belts is threatening ecosystems and their associated natural services, owing to the acceleration of production activities and an energy-consumptive lifestyle within them. Therefore, we should evaluate and predict the impact of green belt releases quantitatively in various fields and deal with these threats to nature conservation and human well-being. Although there have been numerous studies globally on the impact of green belt releases, including in the food, resource, water, biodiversity, real estate, community service and health fields [6–9], there has been a lack of studies aiming to demonstrate its impact on the living environment, especially concerning the climate and air. As awareness increases regarding the fact that land cover change can amplify or mitigate climate change, recently, the number of studies on the evaluation of the interaction between land cover change and climate change has also increased [10–12]. However, there is a shortage of studies evaluating the entire system of green belt release, urban growth, climate change, and air pollution. In this study, we intended to quantify green belt release effects at the local level, based on the interactions among land cover, climate, and air quality. As, however, the effects of the release of green belts becomes more apparent over a longer period of time, it is difficult to prove them conclusively through short-term, empirical observations. Therefore, we deduced long-term effects indirectly, by setting a future target year, defining scenarios, and simulating urban growth and urban environmental changes that would be expected by that year. This study will support policy decision makers in approving or disapproving the release of green belts, by providing more information regarding the changes to the urban environment caused by green belt release. 2. Materials and Methods 2.1. Study Area The South Korean Ministry of Land, Infrastructure and Transport (MOLIT) released the entire green belt (82.6 km2) within Jeju Island, which had been designated and maintained for 30 years, on 4 August 2001. On 13 December 2001, all green belts (291.8 km2) within Chuncheon and some (2.6 km2) in Hongcheon (the administrative district next to Chuncheon) were also released. Using our case studies, we examined urban growth following the release of green belts and its impact on the urban living environment. Jeju and Chuncheon were used as sites for this research (Figure1) as they have the following characteristics: (1) Due to their geographic and environmental isolation, it was possible to perform an accurate impact assessment of green belt releases, as the possibilities of external urban development pressure, or conurbation were low; (2) these regions comprise medium-sized cities, which allowed spatial analysis at a medium-scale resolution. 2.2. Assessment of Effects from the Release of Green Belts The study flow is shown in Figure2, and includes the following six steps: (1) we set up scenarios in which green belts were maintained or released; and (2) estimated the urban region area for the target year, based on increasing trends in the urban area for a certain period of time. (3) Using spatial and statistical techniques, we then analyzed the location characteristics of regions where the land cover was converted into urban land. (4) The probability of the change from non-urban lands to urban lands was estimated based on those characteristics. (5) The estimated probability allowed us to predict changes in the spatial structure within regions released from the green belts by expanding them to the extent of the estimated urban area of the target year. (6) Based on changes in land cover, the ground surface temperature and atmospheric concentrations within those regions were predicted by applying the urban meteorology and climate prediction model. Sustainability 2018, 10, 3260 3 of 21 Sustainability 2018, 10, x FOR PEER REVIEW 3 of 21 Sustainability 2018, 10, x FOR PEER REVIEW 3 of 21 FigureFigureFigure 1. 1.Study 1.Study Study area: area: Jeju Jeju Jejuand and andChuncheon Chuncheon Chuncheon are are medium-sized aremedium-sized medium-sized isolated isolated isolated regions,regions, regions, and green and beltsbelts green withinwithin belts thesewithinthese regionsthese regions which regions which had which had been been had maintained maintained been maintained for for 30 30 years years for 30were were years released released were released totallytotally inin totally the early in the 2000s.2000s. early TheseThese 2000s. regions were used as study sites to prove quantitatively the effect of the release of green belts. regionsThese were regions used were as study used assites study to prove sites toquantitatively prove quantitatively the effect theof the effect release of the of releasegreen belts. of green belts. Figure 2. Flow chart: the main flow of this study is as follows: (1) the set of scenarios, (2) the estimation Figure 2. Flow chart: the main flow of this study is as follows: (1) the set of scenarios, (2) the estimation ofof urban urban area area for for the the target target year, year, (3) the(3) the identification identification oflocation of location characteristics characteristics todetermine to determine land land cover Figure 2. Flow chart: the main flow of this study is as follows: (1) the set of scenarios, (2) the estimation change,cover (4)change, the estimation (4) the estimation of the probability of the probability of conversion of conversion from non-urbanfrom non-urban land intoland urbaninto urban land, land, (5) the of urban area for the target year, (3) the identification of location characteristics to determine land simulation(5) the simulation of urban growthof urban by growth green beltby green release, belt and release, (6) the and simulation (6) the simulation of urban living of urban environment living cover change, (4) the estimation of the probability of conversion from non-urban land into urban land, byenvironment urban growth. by urban growth. (5) the
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