- Open Access
Economic growth for ecological conversions: South Korean case
© The Author(s) 2018
Received: 19 March 2018
Accepted: 6 June 2018
Published: 18 June 2018
Sprawl has been named as one of the critical reasons for the latest social problems in many parts of the world. This is particularly true for developing countries, as their national status largely depends on economic stability and interacts with the rise and decline of major cities. This study focuses on a detailed notion on environmental impact of physical expansion and answers how to specifically estimate the ecological impact of sprawl using the GIS and ecological valuation method. Especially, South Korean cities are examined to identify how development-oriented growth would affect natural stock and the ecology as a whole.
By implementing land cover datasets and an estimation method, value transfer, the authors examine the economic losses of Korean ecological stock between 1980 and 2000. Since 1980, the society has gained a significant amount of growth in its national economics. Specifically, GDP has increased from about $40 billion to $640 billion. However, due to its rapid growth, the entire natural stock has lost about 5% of its total features, using the median economic values. If calculated with the maximum values, it is about a 7% decrease. The results indicate that $2076/person for environmental opportunity costs is estimated as a consequence of rapid urbanization.
If we had estimated the ecological consumptions of rapid growth from the beginning and considered $2076/person for environmental opportunity costs, then the development patterns and other associated urban planning agendas would have shifted accordingly to increase the overall sustainability. Like most developing cities in the world, major cities in South Korea and the central government concentrated its main strategy on economic growth. Doing so stimulated national economy and made it possible to level up the quality of life. If this quality of life needs to be sustained for a long term, then we should focus on our usage of ecological features, as their characteristics are completely different from man-made resources.
Sprawl has been named as one of the critical reasons for the latest social and urban problems in many part of the world. Accordingly, it is a widely studied subject across diverse disciplines [12, 18, 20, 24, 41, 52]. This is particularly true in developing countries, as their national status largely depends on economic stability and strongly interacts with the rise and decline of major cities. As a consequence, a large number of studies have elaborated the effects of urban sprawl, which can be summarized into six aspects: (1) effects of sprawl on public health [3, 14, 19, 23, 35, 44]; (2) on real estate market [4, 6, 42, 43]; (3) on transportation [15–17, 39, 40, 45]; (4) on land use [13, 22, 27, 30, 39]; (5) on the environment [7, 26, 29, 46]; and (6) on urban population .
Of those different perspectives, this study focuses on a more detailed notion of the environmental impact of physical expansion. Because of its unpredictable nature, environmental impact of urban sprawl is often studied using limited externalities such as air pollution, congestion, safety, or noise for the aggregate study areas. The shortcoming of such an approach is that the physical expansion’s specific impact on the ecological features for the selected geographic boundary is generally left behind. To this extent, this study answers how to specifically estimate the ecological impact of sprawl using the geographic information systems (GIS) and ecological valuation method. Especially, South Korean cities are examined to identify how development-oriented direction that is still prevalent in most developing countries would affect natural stock and the ecology as a whole. By implementing different years of land cover datasets and an estimation method, value transfer, the authors examine the economic losses of Korean ecological stock since the 1980s through the 2000s. Doing so provides a brief outline about what are the environmental consequences and responsibilities of becoming one of the fastest growing countries in the world.
Urban sprawl and environmental externalities: the South Korean case
Like many other developing cities in the world, major cities in South Korea have experienced a massive expansion over the past decades. Many reasons can be accounted for this, but during the 1990s it was obvious that the Korean government mainly focused its national strategy on economic growth [32, 36]. Since 1950 when the Korean War ended, it was undoubtedly clear that the socioeconomic status of South Korea was in its deepest downturn. As a response, government officials and associated experts dedicated themselves to improving economic status and concentrating on quantitative growth . This type of approach works mainly for the major cities where the necessary socioeconomic infrastructure is maintained. For that reason, national growth strategy was heavily geared toward large cities across the country.
Specifically, the South Korean government has implemented two major urban developments. Starting in the mid-1990s, the government has constructed new cities in the vicinity of the capital, Seoul. Named as the first generation of the new city model, about six new cities were constructed to accommodate approximately a 1,740,000 population, accounting for about 623,000 households . This development pattern is slightly different from the typical sprawl patterns that took place in the Western Hemisphere, as the density of the new cities was completely different. Because of job–housing imbalance, however, the negative consequences of urban sprawl were found in a similar format. A diverse range of impacts of sprawl such as traffic congestion, travel time increase, carbon emissions, expanded social costs and so forth  were detected. Although the first-generation cities were suggested to invigorate national growth and support the massive population expansion, socioeconomic problems were generated in the same dimension as the majority of the world.
To ease the negative consequences of the first-generation cities, the government decided to try a new type of city development and named it the second-generation city model . Unlike its precursors, the second model used a number of different approaches to mingle jobs and housing together in the same political boundary. Strategies such as tax exemption, financial assistance, and property long-term lease were identified to encourage housing–job balance. However, the problem stemmed from the point where housing developments and residential movements happened relatively easier and faster, whereas job relocation was a much slower process . Although the degree of the impact has changed, the South Korean society is again experiencing similar negative externalities of urban sprawl.
Entering the twenty-first century meant a new era for Korean society to pay less attention to its physical growth, but accentuate more on the quality side of its expansion . A number of international indices, such as the Organization for Economic Cooperation and Development (OECD) Better Life Index, have experienced a rapid improvement based on aggressive economic growth . Nonetheless, it was still unclear whether the nation’s development direction fell well with the overall quality of citizens’ life. In addition, more attention has been paid to the environment since the beginning of the twenty-first century, and the degree of our development speed and the amount of physical conversion have been reviewed by many professionals to gauge the overall sustainability of the society [36, 37]. In this context, it would be helpful to analyze how much environmental consumption took place during the growth and understand what urban expansion means in terms of ecological opportunity costs. By doing so, the degree of economic responsibility of converting natural environment into physical expansion could be elaborated.
Ecological value transfer
To capture the details of the associated environmental opportunity costs, this study models land cover difference of South Korea in 1980, 1990, and 2000. The amount of pervious lands converted into impervious surfaces is calculated for 1980, 1990, and 2000. After that, each land cover type is estimated into monetary values to provide the overall costs of any associated ecological losses.
Ecological cost is estimated using an approach known as value transfer. Value transfer is one particular methodology in the discipline of ecosystem valuation. Although location-specific or micro-level valuation studies are in demand, they generally require more intensive datasets and more precise measurements than studies at an aggregate level [33, 50]. Thus, data availability often becomes an issue. To overcome the limitations and keep the focus on project-specific value measurements, researchers in the ecosystem science suggest a secondary analysis method: value transfer [28, 33, 47, 50]. This transfer method involves obtaining an estimate for the economic value of non-market goods or services through the analysis of a single study or group of studies that have been previously carried out to value similar goods or services. When conducting a primary research work where accurate data collection is not strongly feasible, value transfer represents a meaningful “second-best” strategy and starting point for the evaluation of environmental features [10, 25, 28, 50, 51].
Estimating ecological cost using value transfer involves a number of steps. First, land cover types within the study area should be identified, and there are six types in this study. After that, relevant literature works are collected and summarized to identify transferrable values for each land cover. There are various studies and databases delineating the economic values of land covers such as Environmental Valuation Reference Inventory (EVRI), the Ecosystem Services Partnership, and Natural Capital Project. These types of databases with the study results have increased in the past years [1, 2, 9–11, 49, 50], and the validity of assessing the economic costs of each land cover has become more stable.
Value transfer studies summary
Water supply and regulation
Recreation and esthetic
Soil formation and control
Economic values ($/acre/year) for each land cover type
Land cover types
All of the 88 studies have articulated different economic values of each land cover and, thus, their monetizable values are heterogeneous in nature. In this context, it would be appropriate to implement more scrutiny in valuing each land cover. For example, it would be helpful to use the 75‰ values for each land cover, if the number of studies is abundant. However, some land covers, such as the wetlands, have more than 25 studies, whereas some covers, such as open waters, have only 7 study results of their economic values. Therefore, it is hard to specifically identify the majority of values for each cover and, for that reason, the median values would be more logical to use in terms of land cover monetization.
Another piece of information to estimate the opportunity costs of ecological consumptions is acreage. As described in Table 2, the value estimates are based on acreage per year. It means each land cover’s acreage information should be assessed prior to cost estimation. Using GIS land cover dataset, it is possible to pinpoint how much natural land covers are converted to impervious surfaces. The Ministry of Environment in South Korea provides historic land cover datasets, and in this case 30M × 30M land cover is used to calculate the land cover areas. Economic values using the medians are set into per acre information and each land cover’s acreage information could be converted with the number of 30M pixels inside the land cover’s boundary. Once the necessary information is set, GIS can easily calculate the total monetizable values of each land cover by multiplying per acre median values of each land cover with the total acre of each land cover.
Results and discussion
Land cover changes in Korea between 1980 and 2000
Land cover change of South Korea in 1980, 1990, and 2000
Using the information in Tables 2 and 3, ecological opportunity costs can be estimated between the years 1980 and 2000. To properly identify the changes in the costs, all the unit values in Table 2 were converted to $2015 values using the inflation calculator . As previously mentioned, median ecological values are adopted to avoid any extreme cases that may dominate the estimated results.
Pervious covers and opportunity costs change since 1980 through 2000
Acreage and costs difference between 1980 and 2000
Total (except developed)
In sum, the results show that since 1980, South Korea has lost about $269.3 million in ecological opportunity costs and 497,400 acres reduction in terms of pervious coverage within the national boundary. This is a substantial result, as it relates to overall sustainability and effective resource management of the society. If Korean society has gained more economic benefits by sacrificing $269.3 million in ecological stock, this can at least be justified for a better quality of life. Also, if the growth has induced more social as well as financial benefits that are worth more than $269.3 million, then it would have been a discreet decision.
Land cover dataset is provided by the government body every 10 years and, for that reason, tracking down each land cover’s change over time would be a difficult task. However, tracing each land cover’s change over time would provide a substantial amount of information. For example, decreases in pasture are approximately equivalent to the increase in forest between 1980 and 2000. This could be a sign of a change in pasture to forest, as forest is often regarded as a more valuable resource providing more productivity. Articulating such aspect would be an important task for future research and would increase the quality of analysis.
Growth of South Korea between 1980 and 2000
New city implementation and its population
Acreage and costs difference using the maximum values
Total (except developed)
GDP and ecological costs comparison
GDP per capita
Ecological values (median)
− $270 million
Ecological values (maximum)
− $18,445 million
Ecological values per capita (median)
Ecological values per capita (maximum)
It is hard to precisely compare the ecological stock changes with the GDP increase in South Korea with just simple calculations. As GDP per capita is the sum of annual incomes of all working-age citizens or the sum of all the final goods and services produced in the country, simply comparing GDP changes may not capture precise differences in national economy. In addition, value transfer methods contain several internal assumptions that are partly vulnerable when it comes to methodological justifications. Therefore, calculating ecological values may not provide an in-depth insight into environmental planning of South Korea. Nonetheless, in terms of environmental planning, especially in regional planning, there always is a choice that relevant policy makers and stakeholders could ponder.
What if South Korean government decided to construct just the first-generation new towns? What if we could concentrate more on inner city developments, instead of just expanding new human settlements? Since 2010, old cities in South Korea are experiencing a significant decline in their financial, social, cultural, and physical status. Due to the reason that our birth rate is gradually going down, in fact it reached the lowest in 2017, cities are having a difficult time maintaining their infrastructure and financial status. Many cities in inner areas have observed a massive decline in the number of new students in schools, decrease in their tax revenues, increase in infrastructure maintenance, and surplus in housing supply. These are acceptable consequences, considering our dropped rate in new birth. But if the main purpose of urban planning is to provide a considerate perspective on such sensitive issues, we should at least reconsider our past national development strategies and learn from its lessons to avoid any same mistakes that may happen again. This article is designed to provide such perspectives and to help construct a foundation for a more in-depth analysis on environmental policy between the 1980s and the 2000s in South Korea.
This study is designed to assess whether South Korean society is moving to a sustainable stage of its development by looking at economic values of natural capital. Since 1980, the society has gained a significant amount of growth in its national economics. In addition, although the growth rate is gradually decreasing, population also added a large portion to its total. Specifically, GDP has increased from about $40 billion to $640 billion and this is a notable achievement because South Korea experienced a tragic war in 1950 and all of these increases were gained in about 50 years.
However, due to its rapid growth, the loss in ecological stock can be observed as well. While the society has gained over 1000% increase in GDP and revenues, the entire natural stock has lost about 5% of its total features using the median values. If calculated with the maximum values, it moves up to a decrease of 7%. This may be perceived as a minimal change, since the society has gained economic expansion higher than 1000%. However, if we try to understand that some of the ecological features do not have natural elasticity and, thus, the loss of ecosystem may become a permanent injury to our natural system, this 7% could be a significant reduction. In addition, now that most of the developing and developed countries have entered into the era of steady growth and experiencing a long-term economic stagnation, constant losses in ecological features can become a factor that should be taken into consideration when elaborating on future growth. This will be especially true for some indices that specifically focus on the quantitative side of development of a society.
The lost services of ecosystem features can be defined in two ways: (1) ecosystem with permanent injury, and (2) ecosystem with natural recovery [10, 11, 25]. The former concerns the service lost due to human interference that will never be restored, making the damages permanent. The latter describes those features also damaged by human activities, but which can recover with natural elasticity. In the latter case, a lost ecosystem will fully bounce back to its previous condition at some point in the future. Urban decisions are closer to a permanent injury, as the initial investments are intended to be long lasting. Therefore, 7% decrease can become a game changer to the human habitat as well as to the natural environment.
South Korean society is experiencing the benefits of rapid economic growth since 1980 and, as a result, the entire population has earned numerous comforts and convenience as an urbanized society. However, if we had estimated the ecological consumptions of rapid growth from the beginning and considered $2076/person for environmental opportunity costs, then the development patterns and other associated urban planning agendas would have shifted accordingly to increase the overall sustainability. Like most developing cities in the world, major cities in South Korea and the central government concentrated their main strategy on economic growth. Doing so stimulated national economy and made it possible to level up the quality of life. If this quality of life needs to be sustained for a long term, then we should focus on our usage on ecological features as their characteristics are completely different from man-made resources.
The methods implemented in this study do not prove whether or not the environmental policies of South Korea are doing a good job based on the classical inferential statistics, nor do they provide truly marketable values of ecological resources because there is no specific market to trade ecological resources with the “invisible-hands”. However, depicting the circumstances of historic natural resource consumption is still a meaningful attempt. By doing so, Korean environmental policies could gain an alternative perspective on assessing its success. For that reason, this study will be dedicated to policy review studies as well as ecological economics projects.
HKL prepared the entire data analysis and conducted literature reviews, value transfer analysis, and manuscript editing. HYK was in charge of preparing the manuscript and managing the entire research. Both authors read and approved the final manuscript.
All the authors in this manuscript have read SpringerOpen’s guidance on competing interests and indicate that none of the authors have any competing interests in the manuscript.
Availability of data and materials
Materials described in the manuscript, including all relevant raw data, will be freely available to any scientist wishing to use them for non-commercial purposes.
Consent for publication
This study does not contain details, images, or videos relating to individual participants.
Ethics approval and consent to participate
This study does not require an appropriate ethics approval.
There is no funding source to declare.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.
- Bingham G, Bishop R, Brody M, Bromley D, Clark ET, Cooper W, Costanza R, Hale T, Hayden G, Kellert S (1995) Issues in ecosystem valuation: improving information for decision making. Ecol Econ 14(2):73–90View ArticleGoogle Scholar
- Bockstael N, Costanza R, Strand I, Boynton W, Bell K, Wainger L (1995) Ecological economic modeling and valuation of ecosystems. Ecol Econ 14(2):143–159View ArticleGoogle Scholar
- Brueckner JK (2000) Urban Sprawl: diagnosis and remedies. Int Reg Sci Rev 23(2):160–171View ArticleGoogle Scholar
- Brueckner JK, Fansler DA (1983) The economics of urban sprawl: theory and evidence on the spatial sizes of cities. Rev Econ Stat 65:479–482View ArticleGoogle Scholar
- Chung H, Kang JE, Kang TG, Yoon H (2011) Cities and green economy: comparative study of Korea, China, and Japan. Policy Study, Korea Environment Institute, SeoulGoogle Scholar
- Clawson M (1962) Urban sprawl and speculation in suburban land. Land economics 38:99–111View ArticleGoogle Scholar
- Concepción ED, Obrist MK, Moretti M, Altermatt F, Baur B, Nobis MP (2015) Impacts of urban sprawl on species richness of plants, butterflies, gastropods and birds: not only built-up area matters. Urban Ecosyst 19(1):225–242View ArticleGoogle Scholar
- Conservatree (2015) How much paper can be made from a tree? http://conservatree.org/learn/EnviroIssues/TreeStats.shtml. Aug 2014
- Costanza R (2000) Social goals and the valuation of ecosystem services. Ecosystems 3(1):4–10View ArticleGoogle Scholar
- Costanza R, d’Arge R, Groot R, Farber S, Grasso M, Hannon B, Limburg K, Naeem S, O’Neill VR, Paruelo J, Raskin GR, Sutton P, Belt M (1997) The value of the world’s ecosystem services and natural capital. Nature 387:253–260View ArticleGoogle Scholar
- Costanza R, Daly HE (1992) Natural capital and sustainable development. Conserv Biol 6(1):37–46View ArticleGoogle Scholar
- Downs A (1989) The need for a new vision for the development of large US metropolitan areas. In: LeGates RT, Stout F (eds) The city reader, vol 8. Routledge, New York, pp 545–556Google Scholar
- Du J, Thill J-C, Peiser RB, Feng C (2014) Urban land market and land-use changes in post-reform China: a case study of Beijing. Landsc Urban Plann 124:118–128View ArticleGoogle Scholar
- Ewing R, Brownson RC, Berrigan D (2006) Relationship between urban sprawl and weight of United States youth. Am J Prev Med 31(6):464–474View ArticleGoogle Scholar
- Ewing R, Pendall R, Chen D (2003) Measuring sprawl and its transportation impacts. Transp Res Rec 1831:175–183View ArticleGoogle Scholar
- Ewing R, Schmid T, Killingsworth R, Zlot A, Raudenbush S (2008) Relationship between urban sprawl and physical activity, obesity, and morbidity. Springer, Urban Ecology, pp 567–582Google Scholar
- Freilich RH (1998) The land-use implications of transit-oriented development: controlling the demand side of transportation congestion and Urban Sprawl. The Urban Lawyer, Urban Sprawl, pp 547–572Google Scholar
- Freudenberg M (2003) Composite indicators of country performance: a critical assessment. OECD Publishing, ParisView ArticleGoogle Scholar
- Frumkin H (2002) Urban sprawl and public health. Public Health Rep 117(3):201View ArticleGoogle Scholar
- Graymore MLM, Wallis AM, Richards AJ (2009) An index of regional sustainability: a GIS-based multiple criteria analysis decision support system for progressing sustainability. Ecol Complex 6(4):453–462View ArticleGoogle Scholar
- Grekousis G, Mountrakis G (2015) Sustainable development under population pressure: lessons from developed land consumption in the conterminous US. PLoS ONE 10(3):e0119675View ArticleGoogle Scholar
- Grekousis G, Mountrakis G, Kavouras M (2016) Linking MODIS-derived forest and cropland land cover 2011 estimations to socioeconomic and environmental indicators for the European Union’s 28 countries. GISci Remote Sens 53(1):122–146View ArticleGoogle Scholar
- Grekousis G, Photis YN (2014) Analyzing high-risk emergency areas with GIS and neural networks: the case of Athens, Greece. Prof Geogr 66(1):124–137View ArticleGoogle Scholar
- Grimm NB, Faeth SH, Golubiewski NE, Redman CL, Wu J, Bai X, Briggs JM (2008) Global change and the ecology of cities. Science 319(5864):756–760View ArticleGoogle Scholar
- Groot SR, Wilson AM, Boumans MJR (2002) A typology for the classification, description, and valuation of ecosystem functions, goods, and services. Ecol Econ 41:393–408View ArticleGoogle Scholar
- Hamidi S, Ewing R (2014) A longitudinal study of changes in urban sprawl between 2000 and 2010 in the United States. Landsc Urban Plann 128:72–82View ArticleGoogle Scholar
- Hasse JE, Lathrop RG (2003) Land resource impact indicators of urban sprawl. Appl Geogr 23(2):159–175View ArticleGoogle Scholar
- Herrera Environmental Consultants Inc., Northern Economics Inc., Spatial Informatics Group LLC (2004) Ecological economic evaluation, Maury Island, King County, Washington. Department of Natural Resources and Parks, Seattle, p 61Google Scholar
- Inostroza L, Baur R, Csaplovics E (2013) Urban sprawl and fragmentation in Latin America: a dynamic quantification and characterization of spatial patterns. J Environ Manage 115:87–97View ArticleGoogle Scholar
- Irwin EG, Bockstael NE (2004) Land use externalities, open space preservation, and urban sprawl. Reg Sci Urban Econ 34(6):705–725View ArticleGoogle Scholar
- Kalinowski T, Rhyu SY, Croissant A (2015) 2015 South Korea report. Germany, Sustainable Governance IndicatorsGoogle Scholar
- Korea Economic Institute (2012) Korea’s economy. Seoul, Korea Economic Institute, p 28Google Scholar
- Kreuter UP, Harris HG, Matlock MD, Lacey RE (2001) Change in ecosystem service values in the San Antonio Area, Texas. Ecol Econ 39(3):333–346View ArticleGoogle Scholar
- Lee B (2012) Korean version of new town development. Seoul, Korea Research Institute for Human SettlementsGoogle Scholar
- Lopez R (2004) Urban sprawl and risk for being overweight or obese. Am J Public Health 94(9):1574–1579View ArticleGoogle Scholar
- Noland M (2011) Korea’s growth performance: past and future. East-West Center, HonoluluGoogle Scholar
- Organization for Economic Cooperation and Development (2014) OECD economic surveys Korea overview. OECD, SeoulGoogle Scholar
- Organization for Economic Cooperation and Development (2015) OECD Better Life Index. http://www.oecdbetterlifeindex.org/countries/korea/. Accessed. 30 Mar 2016
- Pendall R (1999) Do land-use controls cause sprawl? Environ Plann B 26(4):555–571View ArticleGoogle Scholar
- Rahman MT (2016) Detection of land use/land cover changes and urban sprawl in Al-Khobar, Saudi Arabia: an analysis of multi-temporal remote sensing data. ISPRS Int J Geo-Inf 5(2):15View ArticleGoogle Scholar
- Saisana M, Trarantola S (2002) State-of-the-art report on current methodologies and practices for composite indicator development. European Commission, IspraGoogle Scholar
- Song Y, Knaap G-J (2003) New urbanism and housing values: a disaggregate assessment. J Urban Econ 54(2):218–238View ArticleGoogle Scholar
- Song Y, Zenou Y (2006) Property tax and urban sprawl: theory and implications for US cities. J Urban Econ 60(3):519–534View ArticleGoogle Scholar
- Srinivasan S, O’Fallon LR, Dearry A (2003) Creating healthy communities, healthy homes, healthy people: initiating a research agenda on the built environment and public health. Am J Public Health 93(9):1446–1450View ArticleGoogle Scholar
- Su Q, DeSalvo JS (2008) The effect of transportation subsidies On Urban Sprawl*. J Reg Sci 48(3):567–594View ArticleGoogle Scholar
- Sung CY, Yi Y-J, Li M-H (2013) Impervious surface regulation and urban sprawl as its unintended consequence. Land Use Policy 32:317–323View ArticleGoogle Scholar
- Troy A, Wilson MA (2006) Mapping ecosystem services: practical challenges and opportunities in linking GIS and value transfer. Ecol Econ 60(2):435–449View ArticleGoogle Scholar
- US Inflation Calculator (2015) US Inflation Calculator. http://www.usinflationcalculator.com/. Accessed Oct 2013
- Wilson MA, Hoehn JP (2006) valuing environmental goods and services using benefit transfer: the state-of-the-art and science. Ecol Econ 60(2):335–342View ArticleGoogle Scholar
- Wilson MA, Troy A, Costanza R (2004) The Economic Geography of Ecosystem Goods and Services. In: Dieterich M, Straaten J (eds) Cultural landscapes and land use: the nature conservation-society interface. Kluwer Academic, Boston, pp 69–94View ArticleGoogle Scholar
- Woodward RT, Wui YS (2001) The economic value of wetland services: a meta-analysis. Ecol Econ 37(2):257–270View ArticleGoogle Scholar
- Zhang J, Liu J, Zhai L, Hou W (2016) Implementation of geographical conditions monitoring in Beijing-Tianjin-Hebei, China. ISPRS Int J Geo-Inf 5(6):89View ArticleGoogle Scholar