571 research outputs found

    Coastal vulnerability assessment: a case study in Kien Giang, western part of the Mekong River Delta in Vietnam

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    Climate change, particularly sea-level rise, threatens low-lying coastal systems, such as small islands on coral atolls, and deltas where millions of people are living. The Mekong River Delta is considered especially at risk. Although most of the delta is only a few metres above sea level, there have been few assessments of vulnerability at local scale. The aim of this thesis is to provide quantitative and qualitative information to guide the process of adaptation and provide visualisations that will enhance local authorityโ€™s decision making to adapt to climate change, particularly sea-level rise. It focuses on the seven coastal districts within Kien Giang province in the western, micro-tidal section of the delta. A framework is adopted that integrates biophysical effects and socioeconomic stressors for the case study area and consists of three main components of vulnerability: exposure, sensitivity, and adaptive capacity. The analytical hierarchical process (AHP) method of multi-criteria decision making was integrated directly into a geographic information system (GIS) to derive a composite vulnerability index that indicated areas or hotspots most likely to be vulnerable to sea-level rise. The hierarchical structure comprised three components: exposure, sensitivity and adaptive capacity (level 1); and eight sub-components (level 2): seawater incursion, flood risk, shoreline change, population characteristics, landuse, as well as socioeconomic, infrastructure, and technological capability. The Digital Shoreline Analysis System (DSAS) tool was used to calculate rates of shoreline change along the Kien Giang coast over time in order to derive the shoreline change sub-component that contributed to the exposure component. Beyond this, a further 22 variables (level 3) and 24 sub-variables (level 4) related to vulnerability were also mapped. Based on the weights of variables derived from AHP pair-wise comparisons, a final map was generated to visualise areas reported into five categories of relative vulnerability; very low, low, moderate, high to very high vulnerability. Several regional patterns emerged. Relatively high exposure to seawater incursion, flood risk, and moderate loss of mangroves characterised the coastal fringe of each district. Those areas found to be most sensitive tended to have moderate population density, generally with a large rural population and high proportions of ethnic households with limited availability of agricultural land. Many aspects of adaptive capacity could only be represented at district scale, with the least adaptable areas consisting of large proportions of poor households, low income, and moderate densities of transport, irrigation, and drainage systems. Finally, most coastal districts were determined to be of moderate to relatively high vulnerability, with scattered hotspots along the Kien Giang coast, which coincided with settlement areas. The results obtained, enable identification and prioritisation of the areas, or hotspots most likely to be vulnerable, for which site-specific assessments might further assist the local authorities and communities in better coastal management and conservation. However, the limitations of data accessible at an entire district can influence the outcome. Social vulnerability remains a challenge because it is changing over time and space

    Modelling of River Flow and Sediment Load Based on the Hydrological Behavior Model in Yahagi River Basin, Japan

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    Source: ICHE Conference Archive - https://mdi-de.baw.de/icheArchiv

    The effect of spatial settlement patterns on urban climatology

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    Increasing urbanization, in addition to driving climate change and pollution, can have a profound effect on the ecosystem properties within and even far from urban areas. As such, it is important to understand the energy balance of cities including the extent of its modification by urban form. This PhD thesis examines the effect of spatial settlement pattern on urban climatology. The initial study focussed on UK overpasses of the Moderate Resolution Imaging Spectro-radiometer (MODIS) satellite instrument, covering the period between 2000 and 2017, were sampled to examine the seasonal (winter and summer) night-time clear-sky upwelling long-wave energy for 35 UK cities. Total (area-summed) emitted energy was calculated per city. Well-defined (R2โ‰ฅ0.79) and robust โ€˜allometricโ€™ scaling against city population was found for all samples. Total night-time emitted energy is found to scale sub-linearly with population on both summer and winter nights, with slope of 0.85ยฑ0.03. The scaling of night-time emitted energy with urban areas is close to linear (1.0ยฑ0.05). This indicates that UK Cities, although often appearing superficially very different, are similar in their gross thermal properties, i.e., in terms of the components of urban form, which dictate thermal properties. A case study of Nigeriaโ€™s cities on allometric scaling of emitted energy with population is also investigated, and it turned out to be very different from the UK study with slope of 0.41ยฑ0.05. Nigerian cities show much more sub-linear allometric scaling of total emitted energy with population, indicating slightly economy of scale in terms of nocturnal heat production. Local climate zones are further used to interpret results from the study. The study went further to investigate how the sum measure of the spatial distribution of emitted energy inside the cityโ€™s boundary is affected by the urban morphology, using the previous UK study. A fitted distribution of both extremesโ€™ percentiles of emitted energy and land use maps within city were used as basis for comparison across cities in order to delineate the hottest and coldest spots in the distribution of long-wave energy for a sample night

    ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜์„ ์ด์šฉํ•œ ๋‹ค์ค‘์Šค์ผ€์ผ/๋‹ค๋ชฉ์  ๊ณต๊ฐ„๊ณ„ํš ์ตœ์ ํ™”๋ชจ๋ธ ๊ตฌ์ถ•

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    ํ•™์œ„๋…ผ๋ฌธ (๋ฐ•์‚ฌ)-- ์„œ์šธ๋Œ€ํ•™๊ต ๋Œ€ํ•™์› : ํ™˜๊ฒฝ๋Œ€ํ•™์› ํ˜‘๋™๊ณผ์ • ์กฐ๊ฒฝํ•™์ „๊ณต, 2019. 2. ์ด๋™๊ทผ.๊ณต๊ฐ„๊ณ„ํš ๊ณผ์ •์—์„œ ๋‹ค์–‘ํ•œ ์ดํ•ด๊ด€๊ณ„์ž์™€ ๊ฒฐ๋ถ€๋œ ๋ชฉํ‘œ์™€ ์ œ์•ฝ ์š”๊ฑด์„ ๋งŒ์กฑ์‹œํ‚ค๋Š” ๊ฒƒ์€ ๋ณต์žกํ•œ ๋น„์„ ํ˜•์  ๋ฌธ์ œ๋กœ์„œ ํ•ด๊ฒฐํ•˜๊ธฐ ์–ด๋ ค์šด ๊ฒƒ์œผ๋กœ ์•Œ๋ ค์ ธ ์™”๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ์ตœ๊ทผ ์ด๋Ÿฌํ•œ ๋ฌธ์ œ์— ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜ (genetic algorithms), ๋‹ด๊ธˆ์งˆ ๊ธฐ๋ฒ• (simulated annealing), ๊ฐœ๋ฏธ ๊ตฐ์ง‘ ์ตœ์ ํ™” (ant colony optimization) ๋“ฑ์˜ ๋‹ค๋ชฉ์  ์ตœ์ ํ™” ์•Œ๊ณ ๋ฆฌ์ฆ˜์ด ์‘์šฉ๋˜๊ณ  ์žˆ์œผ๋ฉฐ, ๊ด€๋ จ ์—ฐ๊ตฌ ์—ญ์‹œ ๊ธ‰์ฆํ•˜๊ณ  ์žˆ๋‹ค. ์ด ์ค‘ ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜์€ ๊ณต๊ฐ„ ์ตœ์ ํ™” ๋ถ€๋ฌธ์— ๊ฐ€์žฅ ๋นˆ๋„ ๋†’๊ฒŒ ์ ์šฉ๋œ ์ตœ์ ํ™” ์•Œ๊ณ ๋ฆฌ์ฆ˜์œผ๋กœ exploration๊ณผ exploitation์˜ ๊ท ํ˜•์œผ๋กœ ํ•ฉ๋ฆฌ์ ์ธ ์‹œ๊ฐ„ ๋‚ด์— ์ถฉ๋ถ„ํžˆ ์ข‹์€ ๊ณ„ํš์•ˆ์„ ์ œ์‹œํ•  ์ˆ˜ ์žˆ๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ๊ณต๊ฐ„ ์ตœ์ ํ™” ์—ฐ๊ตฌ๊ฐ€ ๋ณด์—ฌ์ค€ ์ข‹์€ ์„ฑ๊ณผ์—๋„ ๋ถˆ๊ตฌํ•˜๊ณ  ๋Œ€๋ถ€๋ถ„์˜ ์—ฐ๊ตฌ๊ฐ€ ํŠน์ • ์šฉ๋„ ํ˜น์€ ์‹œ์„ค์˜ ๋ฐฐ์น˜์— ์ง‘์ค‘๋˜์–ด ์žˆ์œผ๋ฉฐ, ๊ธฐํ›„๋ณ€ํ™” ์ ์‘, ์žฌํ•ด ๊ด€๋ฆฌ, ๊ทธ๋ฆฐ์ธํ”„๋ผ ๊ณ„ํš๊ณผ ๊ฐ™์€ ์ตœ๊ทผ์˜ ํ™˜๊ฒฝ ์ด์Šˆ๋ฅผ ๋‹ค๋ฃฌ ์‚ฌ๋ก€๋Š” ๋งค์šฐ ๋ฏธํกํ•˜๋‹ค. ๋”ฐ๋ผ์„œ ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜๊ณผ ๋น„์ง€๋ฐฐ ์ •๋ ฌ ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜ (non-dominated sorting genetic algorithm II)์— ๊ธฐ์ดˆํ•˜์—ฌ ๊ธฐํ›„๋ณ€ํ™” ์ ์‘, ์žฌํ•ด ๊ด€๋ฆฌ, ๋„์‹œ์˜ ๋…น์ง€ ๊ณ„ํš ๋“ฑ๊ณผ ๊ฐ™์€ ํ™˜๊ฒฝ ์ด์Šˆ๋ฅผ ๊ณต๊ฐ„๊ณ„ํš์— ๋ฐ˜์˜ํ•  ์ˆ˜ ์žˆ๋Š” ์ผ๋ จ์˜ ๊ณต๊ฐ„ ์ตœ์ ํ™” ๋ชจ๋ธ์„ ์ œ์‹œํ•˜์˜€๋‹ค. ๊ฐœ๋ณ„ ํ™˜๊ฒฝ ์ด์Šˆ์— ๋”ฐ๋ผ ๊ณต๊ฐ„ ํ•ด์ƒ๋„, ๋ชฉ์ , ์ œ์•ฝ์š”๊ฑด์ด ๋‹ค๋ฅด๊ฒŒ ๊ตฌ์„ฑํ•˜์˜€์œผ๋ฉฐ, ๊ณต๊ฐ„์  ๋ฒ”์œ„๊ฐ€ ์ข์•„์ง€๊ณ  ๊ณต๊ฐ„ํ•ด์ƒ๋„๋Š” ๋†’์•„์ง€๋Š” ์ˆœ์„œ๋Œ€๋กœ ๋‚˜์—ดํ•˜์˜€๋‹ค. ๋…ผ๋ฌธ์˜ ์ฒซ๋ฒˆ์งธ ์žฅ์—์„œ๋Š” ํ–‰์ •๊ตฌ์—ญ ๋„ ๊ทœ๋ชจ (province scale, ํ•ด์ƒ๋„ 1ใŽข)์—์„œ ๋ฏธ๋ž˜์˜ ๊ธฐํ›„๋ณ€ํ™”์— ์ ์‘ํ•˜๊ธฐ ์œ„ํ•œ ํ† ์ง€์ด์šฉ ์‹œ๋‚˜๋ฆฌ์˜ค๋ฅผ ๋ชจ์˜ํ•  ์ˆ˜ ์žˆ๋Š” ๊ณต๊ฐ„ ์ตœ์ ํ™” ๋ชจ๋ธ์„ ์ œ์•ˆํ•˜์˜€๋‹ค. ๊ธฐํ›„๋ณ€ํ™”๊ฐ€ ๋จผ ๋ฏธ๋ž˜๊ฐ€ ์•„๋‹Œ, ํ˜„์žฌ ์ด๋ฏธ ์ง„ํ–‰๋˜๊ณ  ์žˆ์œผ๋ฉฐ ๊ด€๋ จํ•œ ๋‹ค์ˆ˜์˜ ํ”ผํ•ด๊ฐ€ ๊ด€์ฐฐ๋˜๊ณ  ์žˆ๊ธฐ ๋•Œ๋ฌธ์— ๊ณต๊ฐ„์  ๊ด€์ ์—์„œ ๊ธฐํ›„๋ณ€ํ™”์— ๋Œ€ํ•œ ์ ์‘์˜ ํ•„์š”์„ฑ์ด ์ง€์ ๋˜์–ด ์™”๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ๊ตฌ์ฒด์ ์œผ๋กœ ๊ธฐํ›„์— ๋Œ€ํ•œ ํšŒ๋ณต ํƒ„๋ ฅ์„ฑ์„ ํ–ฅ์ƒ์‹œํ‚ค๊ธฐ ์œ„ํ•˜์—ฌ ํ† ์ง€์ด์šฉ์˜ ๊ณต๊ฐ„์  ๊ตฌ์„ฑ์„ ์–ด๋–ป๊ฒŒ ๋ณ€ํ™”์‹œ์ผœ์•ผ ํ• ์ง€์— ๋Œ€ํ•œ ๋ฐฉ๋ฒ•๋ก  ์ œ์‹œ๋Š” ๋ฏธํกํ•˜๋‹ค. ์ง€์—ญ๊ณ„ํš์—์„œ ๊ธฐํ›„๋ณ€ํ™” ์˜ํ–ฅ์„ ๊ณ ๋ คํ•œ ํ† ์ง€์ด์šฉ ๋ฐฐ๋ถ„์€ ๋งค์šฐ ์œ ์šฉํ•œ, ๊ธฐ๋ณธ์ ์ธ ์ค‘์žฅ๊ธฐ ์ ์‘ ์ „๋žต์— ํ•ด๋‹นํ•œ๋‹ค. ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ๋‹ค๋ชฉ์  ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜ (MOGA, multi-objective genetic algorithm)์— ๊ธฐ์ดˆํ•˜์—ฌ 9,982ใŽข์— 350๋งŒ์˜ ์ธ๊ตฌ๊ฐ€ ๊ฑฐ์ฃผํ•˜๋Š” ํ•œ๊ตญ์˜ ์ถฉ์ฒญ๋‚จ๋„ ๋ฐ ๋Œ€์ „๊ด‘์—ญ์‹œ ์ผ๋Œ€๋ฅผ ๋Œ€์ƒ์œผ๋กœ ๊ธฐํ›„๋ณ€ํ™” ์ ์‘์„ ์œ„ํ•œ ํ† ์ง€์ด์šฉ ์‹œ๋‚˜๋ฆฌ์˜ค๋ฅผ ์ œ์‹œํ•˜์˜€๋‹ค. ์ง€์—ญ์ ์ธ ๊ธฐํ›„๋ณ€ํ™” ์˜ํ–ฅ๊ณผ ๊ฒฝ์ œ์  ์—ฌ๊ฑด์„ ๊ณ ๋ คํ•˜์—ฌ ์žฌํ•ด ํ”ผํ•ด ๋ฐ ์ „ํ™˜๋Ÿ‰์˜ ์ตœ์†Œํ™”, ๋ฒผ ์ƒ์‚ฐ๋Ÿ‰, ์ข… ํ’๋ถ€๋„ ๋ณด์ „, ๊ฒฝ์ œ์  ๊ฐ€์น˜์˜ ์ตœ๋Œ€ํ™” ๋“ฑ ๋‹ค์„ฏ ๊ฐ€์ง€์˜ ๋ชฉ์ ์„ ์„ ํƒํ•˜์˜€๋‹ค. ๊ฐ ๋ชฉ์  ๋ณ„ ๊ฐ€์ค‘์น˜๋ฅผ ๋ณ€ํ™”์‹œํ‚ค๋ฉฐ ์—ฌ์„ฏ ๊ฐ€์ง€ ๊ฐ€์ค‘์น˜ ์กฐํ•ฉ์— ๋Œ€ํ•œ 17๊ฐœ์˜ ํŒŒ๋ ˆํ†  ์ตœ์  ํ† ์ง€์ด์šฉ ์‹œ๋‚˜๋ฆฌ์˜ค๋ฅผ ์ƒ์„ฑํ•˜์˜€๋‹ค. ๋Œ€๋ถ€๋ถ„์˜ ์‹œ๋‚˜๋ฆฌ์˜ค๋Š” ์ •๋„์˜ ์ฐจ์ด๋Š” ์žˆ์œผ๋‚˜ ํ˜„์žฌ์˜ ํ† ์ง€์ด์šฉ์— ๋น„ํ•ด ๊ธฐํ›„๋ณ€ํ™” ์ ์‘ ๋ถ€๋ถ„์—์„œ ๋” ์ข‹์€ ํผํฌ๋จผ์Šค๋ฅผ ๋ณด์˜€์œผ๋ฏ€๋กœ, ๊ธฐํ›„๋ณ€ํ™”์— ๋Œ€ํ•œ ํšŒ๋ณตํƒ„๋ ฅ์„ฑ์ด ๊ฐœ์„ ํ•  ์ˆ˜ ์žˆ์„ ๊ฒƒ์œผ๋กœ ํŒ๋‹จํ•˜์˜€๋‹ค. ๋˜ํ•œ ๊ณต๊ฐ„ ์ตœ์ ํ™” ๋ชจ๋ธ์˜ ์œ ์—ฐํ•œ ๊ตฌ์กฐ๋ฅผ ๊ณ ๋ คํ•˜์˜€์„ ๋•Œ, ์ง€์—ญ์˜ ์‹ค๋ฌด์ž ์—ญ์‹œ ๊ฐ€์ค‘์น˜์™€ ๊ฐ™์€ ๋ชจ๋ธ์˜ ํŒŒ๋ผ๋ฏธํ„ฐ, ๊ธฐํ›„๋ณ€ํ™” ์˜ํ–ฅ ํ‰๊ฐ€์™€ ๊ฐ™์€ ์ž…๋ ฅ์ž๋ฃŒ๋ฅผ ๋ณ€๊ฒฝํ•จ์œผ๋กœ์จ ํšจ์œจ์ ์œผ๋กœ ์ƒˆ๋กœ์šด ์‹œ๋‚˜๋ฆฌ์˜ค๋ฅผ ์ƒ์„ฑ ๋ฐ ์„ ํƒํ•˜๋Š” ๊ฒƒ์ด ๊ฐ€๋Šฅํ•  ๊ฒƒ์œผ๋กœ ์˜ˆ์ƒํ•˜์˜€๋‹ค. ๋…ผ๋ฌธ์˜ ๋‘ ๋ฒˆ์งธ ์žฅ์—์„œ๋Š” ํ–‰์ •๊ตฌ์—ญ ๊ตฐ ๊ทœ๋ชจ (local scale, ํ•ด์ƒ๋„ 100m)์—์„œ ๊ธฐํ›„๋ณ€ํ™”์— ๋”ฐ๋ฅธ ์žฌํ•ด ํ”ผํ•ด๋ฅผ ๊ด€๋ฆฌํ•˜๊ธฐ ์œ„ํ•œ ํ† ์ง€์ด์šฉ ์‹œ๋‚˜๋ฆฌ์˜ค๋ฅผ ๋ชจ์˜ํ•  ์ˆ˜ ์žˆ๋Š” ๊ณต๊ฐ„ ์ตœ์ ํ™” ๋ชจ๋ธ์„ ์ œ์•ˆํ•˜์˜€๋‹ค. ์‚ฐ์•…์ง€ํ˜•์—์„œ ํญ์šฐ๋กœ ์ธํ•œ ์‚ฐ์‚ฌํƒœ๋Š” ์ธ๋ช…๊ณผ ์žฌ์‚ฐ์— ์‹ฌ๊ฐํ•œ ํ”ผํ•ด๋ฅผ ์ดˆ๋ž˜ํ•  ์ˆ˜ ์žˆ๋Š” ๊ฒƒ์œผ๋กœ ์•Œ๋ ค์ ธ ์žˆ๋‹ค. ๋”์šฑ์ด ๊ธฐํ›„๋ณ€ํ™”์— ๋”ฐ๋ฅธ ๊ฐ•์šฐ์˜ ๋ณ€๋™์„ฑ ์ฆ๊ฐ€๋กœ ์ด๋Ÿฌํ•œ ์‚ฐ์‚ฌํƒœ ๋นˆ๋„ ๋ฐ ๊ฐ•๋„ ์—ญ์‹œ ์ฆ๋Œ€๋  ๊ฒƒ์œผ๋กœ ์˜ˆ์ƒ๋œ๋‹ค. ์ผ๋ฐ˜์ ์œผ๋กœ ์‚ฐ์‚ฌํƒœ ๋ฆฌ์Šคํฌ๊ฐ€ ๋†’์€ ์ง€์—ญ์„ ํ”ผํ•ด ๊ฐœ๋ฐœ์ง€์—ญ์„ ๋ฐฐ์น˜ํ•˜๋Š” ๊ฒƒ์ด ํ”ผํ•ด๋ฅผ ์ €๊ฐ ํ˜น์€ ํšŒํ”ผํ•  ์ˆ˜ ์žˆ๋Š” ๊ฐ€์žฅ ํšจ๊ณผ์ ์ธ ์ „๋žต์œผ๋กœ ์•Œ๋ ค์ ธ ์žˆ์œผ๋‚˜, ์‹ค์ œ๊ณต๊ฐ„์—์„œ์˜ ๊ณ„ํš์€ ๋งค์šฐ ๋ณต์žกํ•œ ๋น„์„ ํ˜•์˜ ๋ฌธ์ œ๋กœ์„œ ์ด๊ฒƒ์„ ์‹คํ˜„ํ•˜๋Š” ๋ฐ ์–ด๋ ค์›€์ด ์žˆ๋‹ค. ๋”ฐ๋ผ์„œ ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ๋น„์ง€๋ฐฐ ์ •๋ ฌ ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜ II์— ๊ธฐ์ดˆํ•˜์—ฌ ์‚ฐ์‚ฌํƒœ ๋ฆฌ์Šคํฌ ๋ฐ ์ „ํ™˜๋Ÿ‰, ํŒŒํŽธํ™”์˜ ์ตœ์†Œํ™” ๋“ฑ์˜ ๋‹ค์–‘ํ•œ ๋ชฉ์ ์„ ๋งŒ์กฑ์‹œํ‚ค๋Š” ์ข…ํ•ฉ์ ์ธ ํ† ์ง€์ด์šฉ ๋ฐฐ๋ถ„ ๊ณ„ํš์„ ์ œ์•ˆํ•˜์˜€๋‹ค. ๋Œ€์ƒ์ง€๋Š” 2018๋…„ ๋™๊ณ„์˜ฌ๋ฆผํ”ฝ ๊ฐœ์ตœ์ง€์ธ ํ•œ๊ตญ์˜ ํ‰์ฐฝ๊ตฐ์œผ๋กœ์„œ 2006๋…„์— ์‚ฐ์‚ฌํƒœ๋กœ ์ธํ•œ ๋Œ€๊ทœ๋ชจ์˜ ํ”ผํ•ด๋ฅผ ๊ฒฝํ—˜ํ•˜์˜€์œผ๋‚˜, ์˜ฌ๋ฆผํ”ฝ ํŠน์ˆ˜ ๋“ฑ์˜ ๊ฐœ๋ฐœ์••๋ ฅ์œผ๋กœ ์ธํ•œ ๋‚œ๊ฐœ๋ฐœ์ด ์šฐ๋ ค๋˜๋Š” ์ง€์—ญ์ด๋‹ค. ์ตœ์ข…์ ์œผ๋กœ ํ•œ๋ฒˆ์˜ ๋ชจ์˜๋ฅผ ํ†ตํ•ด ํ˜„์žฌ์˜ ํ† ์ง€์ด์šฉ ๋ณด๋‹ค ์ ์–ด๋„ ํ•œ๊ฐ€์ง€ ์ด์ƒ์˜ ๋ชฉ์ ์—์„œ ์ข‹์€ ํผํฌ๋จผ์Šค๋ฅผ ๋ณด์ด๋Š” 100๊ฐœ์˜ ํŒŒ๋ ˆํ†  ์ตœ์  ๊ณ„ํš์•ˆ์„ ์ƒ์„ฑํ•˜์˜€๋‹ค. ๋˜ํ•œ 5๊ฐœ์˜ ๋Œ€ํ‘œ์ ์ธ ๊ณ„ํš์•ˆ์„ ์„ ์ •ํ•˜์—ฌ ์‚ฐ์‚ฌํƒœ๋ฆฌ์Šคํฌ ์ตœ์†Œํ™”์™€ ์ „ํ™˜๋Ÿ‰ ์ตœ์†Œํ™” ๊ฐ„์— ๋ฐœ์ƒํ•˜๋Š” ์ƒ์‡„ ํšจ๊ณผ๋ฅผ ์„ค๋ช…ํ•˜์˜€๋‹ค. ๋ณธ ์—ฐ๊ตฌ๊ฒฐ๊ณผ๋Š” ๊ธฐํ›„๋ณ€ํ™”์™€ ๊ด€๋ จ๋œ ๊ณต๊ฐ„ ์ ์‘ ์ „๋žต์˜ ์ˆ˜๋ฆฝ, ๋ณด๋‹ค ํ–ฅ์ƒ๋œ ๊ฐœ๋ฐœ๊ณ„ํš์„ ์œ„ํ•œ ์˜์‚ฌ๊ฒฐ์ •์„ ํšจ๊ณผ์ ์œผ๋กœ ์ง€์›ํ•  ์ˆ˜ ์žˆ์„ ๊ฒƒ์œผ๋กœ ์˜ˆ์ƒํ•˜์˜€๋‹ค. ๋…ผ๋ฌธ์˜ ์„ธ ๋ฒˆ์งธ ์žฅ์—์„œ๋Š” ๋ธ”๋ก ๊ทœ๋ชจ(neighborhood scale, 2m)์—์„œ ๋„์‹œ ๋‚ด ๋…น์ง€๊ณ„ํš์•ˆ์„ ๋ชจ์˜ํ•  ์ˆ˜ ์žˆ๋Š” ๊ณต๊ฐ„ ์ตœ์ ํ™” ๋ชจ๋ธ์„ ์ œ์•ˆํ•˜์˜€๋‹ค. ๋…น์ง€ ๊ณต๊ฐ„์€ ๋„์‹œ๋ฏผ์˜ ์‚ถ์˜ ์งˆ์— ๊ฒฐ์ •์ ์ธ ์˜ํ–ฅ์„ ๋ฏธ์น˜๊ธฐ ๋•Œ๋ฌธ์— ๋‹ค์–‘ํ•œ ๋„์‹œ ์žฌ์ƒ ๋ฐ ๊ฐœ๋ฐœ๊ณ„ํš์—๋Š” ๋…น์ง€์™€ ์ง ๊ฐ„์ ‘์ ์œผ๋กœ ๊ด€๋ จ๋œ ์ „๋žต์ด ํฌํ•จ๋œ๋‹ค. ๋…น์ง€ ๊ณต๊ฐ„์€ ๋„์‹œ์ง€์—ญ ๋‚ด์—์„œ ์—ด์„ฌ ํ˜„์ƒ ์™„ํ™”, ์œ ์ถœ๋Ÿ‰ ์ €๊ฐ, ์ƒํƒœ ๋„คํŠธ์›Œํฌ ์ฆ์ง„ ๋“ฑ ๋‹ค์–‘ํ•œ ๊ธ์ •์  ํšจ๊ณผ๊ฐ€ ์žˆ์Œ์ด ์•Œ๋ ค์ ธ ์žˆ์œผ๋‚˜, ๊ณต๊ฐ„ ๊ณ„ํš์˜ ๊ด€์ ์—์„œ ์ด๋Ÿฌํ•œ ๋‹ค์–‘ํ•œ ํšจ๊ณผ๋ฅผ ์ข…ํ•ฉ์ , ์ •๋Ÿ‰์ ์œผ๋กœ ๊ณ ๋ ค๋œ ์‚ฌ๋ก€๋Š” ๋งค์šฐ ๋ฏธํกํ•˜๋‹ค. ๋”ฐ๋ผ์„œ ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ๋น„์ง€๋ฐฐ ์ •๋ ฌ ์œ ์ „ ์•Œ๊ณ ๋ฆฌ์ฆ˜ II์— ๊ธฐ์ดˆํ•˜์—ฌ ๋…น์ง€์˜ ์ƒํƒœ์  ์—ฐ๊ฒฐ์„ฑ ์ฆ์ง„, ์—ด์„ฌ ํšจ๊ณผ ์™„ํ™”์™€ ๊ฐ™์€ ๋‹ค์–‘ํ•œ ํšจ๊ณผ์™€ ์„ค์น˜์— ๋”ฐ๋ฅด๋Š” ๋น„์šฉ์„ ์ข…ํ•ฉ์ ์œผ๋กœ ๊ณ ๋ คํ•˜์—ฌ ์ ์ ˆํ•œ ๋…น์ง€์˜ ์œ ํ˜•๊ณผ ์œ„์น˜๋ฅผ ๊ฒฐ์ •ํ•œ ๋…น์ง€๊ณ„ํš์•ˆ์„ ์ œ์‹œํ•˜์˜€๋‹ค. ๋ธ”๋ก ๊ทœ๋ชจ์˜ ๊ฐ€์ƒ์˜ ๋Œ€์ƒ์ง€์— ๋ณธ ์ตœ์ ํ™” ๋ชจ๋ธ์„ ์ ์šฉํ•จ์œผ๋กœ์จ 30๊ฐœ์˜ ํŒŒ๋ ˆํ†  ์ตœ์  ๋…น์ง€๊ณ„ํš์•ˆ์„ ์ƒ์„ฑํ•˜์˜€์œผ๋ฉฐ, ๊ฐ ๋ชฉ์  ๊ฐ„ ํผํฌ๋จผ์Šค๋ฅผ ๋น„๊ตํ•˜์—ฌ ๋…น์ง€์˜ ์—ด์„ฌ ์™„ํ™” ํšจ๊ณผ์™€ ์ƒํƒœ์  ์—ฐ๊ฒฐ์„ฑ ์ฆ์ง„ ํšจ๊ณผ ๊ฐ„์˜ ์ƒ์Šน ๊ด€๊ณ„ (synergistic relationship), ์ด๋Ÿฌํ•œ ๊ธ์ •์  ํšจ๊ณผ์™€ ๋น„์šฉ ์ ˆ๊ฐ ๊ฐ„์˜ ์ƒ์‡„ ํšจ๊ณผ (trade-off relationship)๋ฅผ ๋ถ„์„ํ•˜์˜€๋‹ค. ๋˜ํ•œ ๋‹ค์–‘ํ•œ ๊ณ„ํš์•ˆ ์ค‘ ๋Œ€ํ‘œ์ ์ธ ํŠน์„ฑ์„ ์ง€๋‹ˆ๋Š” ๊ณ„ํš์•ˆ, ๋‹ค์ˆ˜์˜ ๊ณ„ํš์•ˆ์—์„œ ๊ณตํ†ต์ ์œผ๋กœ ๋…น์ง€ ์„ค์น˜๋ฅผ ์œ„ํ•ด ์„ ํƒ๋œ ์ฃผ์š” ํ›„๋ณด์ง€์—ญ ์—ญ์‹œ ๊ทœ๋ช…ํ•˜์˜€๋‹ค. ๋ณธ ์—ฐ๊ตฌ์—์„œ ์ œ์‹œ๋œ ๋ชจ๋ธ์€ ๊ณ„ํš์•ˆ์˜ ์ˆ˜์ •์—์„œ๋ถ€ํ„ฐ ์ •๋Ÿ‰์  ํ‰๊ฐ€, ๊ณ„ํš์•ˆ ์„ ํƒ์— ์ด๋ฅด๋Š” ์ผ๋ จ์˜ ๊ธ์ •์ ์ธ ํ”ผ๋“œ๋ฐฑ ๊ณผ์ •์„ ์ˆ˜์—†์ด ๋ฐ˜๋ณตํ•จ์œผ๋กœ์จ ๊ธฐ์กด์˜ ๋…น์ง€๊ณ„ํš ๊ณผ์ •์„ ๊ฐœ์„ ํ•˜๋Š” ๋ฐ ๊ธฐ์—ฌํ•  ์ˆ˜ ์žˆ์„ ๋ฟ๋งŒ ์•„๋‹ˆ๋ผ ๋ชจ๋ธ์˜ ๊ฒฐ๊ณผ ์—ญ์‹œ ๋‹ค์ž๊ฐ„ ํ˜‘๋ ฅ์  ๋””์ž์ธ (co-design)์„ ์œ„ํ•œ ์ดˆ์•ˆ์œผ๋กœ์„œ ํ™œ์šฉ๋  ์ˆ˜ ์žˆ์„ ๊ฒƒ์œผ๋กœ ์˜ˆ์ƒํ•˜์˜€๋‹ค.The meeting of heterogeneous goals while staying within the constraints of spatial planning is a nonlinear problem that cannot be solved by linear methodologies. Instead, this problem can be solved using multi-objective optimization algorithms such as genetic algorithms (GA), simulated annealing (SA), ant colony optimization (ACO), etc., and research related to this field has been increasing rapidly. GA, in particular, are the most frequently applied spatial optimization algorithms and are known to search for a good solution within a reasonable time period by maintaining a balance between exploration and exploitation. However, despite its good performance and applicability, it has not adequately addressed recent urgent issues such as climate change adaptation, disaster management, and green infrastructure planning. It is criticized for concentrating on only the allocation of specific land use such as urban and protected areas, or on the site selection of a specific facility. Therefore, in this study, a series of spatial optimizations are proposed to address recent urgent issues such as climate change, disaster management, and urban greening by supplementing quantitative assessment methodologies to the spatial planning process based on GA and Non-dominated Sorting Genetic Algorithm II (NSGA II). This optimization model needs to be understood as a tool for providing a draft plan that quantitatively meets the essential requirements so that the stakeholders can collaborate smoothly in the planning process. Three types of spatial planning optimization models are classified according to urgent issues. Spatial resolution, planning objectives, and constraints were also configured differently according to relevant issues. Each spatial planning optimization model was arranged in the order of increasing spatial resolution. In the first chapter, the optimization model was proposed to simulate land use scenarios to adapt to climate change on a provincial scale. As climate change is an ongoing phenomenon, many recent studies have focused on adaptation to climate change from a spatial perspective. However, little is known about how changing the spatial composition of land use could improve resilience to climate change. Consideration of climate change impacts when spatially allocating land use could be a useful and fundamental long-term adaptation strategy, particularly for regional planning. Here climate adaptation scenarios were identified on the basis of existing extents of three land use classes using Multi-objective Genetic Algorithms (MOGA) for a 9,982 km2 region with 3.5 million inhabitants in South Korea. Five objectives were selected for adaptation based on predicted climate change impacts and regional economic conditions: minimization of disaster damageand existing land use conversionmaximization of rice yieldprotection of high-species-richness areasand economic value. The 17 Pareto land use scenarios were generated by six weighted combinations of the adaptation objectives. Most scenarios, although varying in magnitude, showed better performance than the current spatial land use composition for all adaptation objectives, suggesting that some alteration of current land use patterns could increase overall climate resilience. Given the flexible structure of the optimization model, it is expected that regional stakeholders would efficiently generate other scenarios by adjusting the model parameters (weighting combinations) or replacing the input data (impact maps) and selecting a scenario depending on their preference or a number of problem-related factors. In the second chapter, the optimization model was proposed to simulate land use scenarios for managing disaster damage due to climate change on local scale. Extreme landslides triggered by rainfall in hilly regions frequently lead to serious damage, including casualties and property loss. The frequency of landslides may increase under climate change, because of the increased variability of precipitation. Developing urban areas outside landslide risk zones is the most effective method of reducing or preventing damageplanning in real life is, however, a complex and nonlinear problem. For such multi-objective problems, GA may be the most appropriate optimization tool. Therefore, comprehensive land use allocation plans were suggested using the NSGA II to overcome multi-objective problems, including the minimization of landslide risk, minimization of change, and maximization of compactness. The study area is Pyeongchang-gun, the host city of the 2018 Winter Olympics in Korea, where high development pressure has resulted in an urban sprawl into the hazard zone that experienced a large-scale landslide in 2006. We obtained 100 Pareto plans that are better than the actual land use data for at least one objective, with five plans that explain the trade-offs between meeting the first and the second objectives mentioned above. The results can be used by decision makers for better urban planning and for climate change-related spatial adaptation. In the third chapter, the optimization model was proposed to simulate urban greening plans on a neighborhood scale. Green space is fundamental to the good quality of life of residents, and therefore urban planning or improvement projects often include strategies directly or indirectly related to greening. Although green spaces generate positive effects such as cooling and reduction of rainwater runoff, and are an ecological corridor, few studies have examined the comprehensive multiple effects of greening in the urban planning context. To fill this gap in this fields literature, this study seeks to identify a planning model that determines the location and type of green cover based on its multiple effects (e.g., cooling and enhancement of ecological connectivity) and the implementation cost using NSGA II. The 30 Pareto-optimal plans were obtained by applying our model to a hypothetical landscape on a neighborhood scale. The results showed a synergistic relationship between cooling and enhancement of connectivity, as well as a trade-off relationship between greenery effects and implementation cost. It also defined critical lots for urban greening that are commonly selected in various plans. This model is expected to contribute to the improvement of existing planning processes by repeating the positive feedback loop: from plan modification to quantitative evaluation and selection of better plans. These optimal plans can also be considered as options for co-design by related stakeholders.1. INTRODUCTION 2. CHAPTER 1: Modelling Spatial Climate Change Land use Adaptation with Multi-Objective Genetic Algorithms to Improve Resilience for Rice Yield and Species Richness and to Mitigate Disaster Risk 2.1. Introduction 2.2. Study area 2.3. Methods 2.4. Results 2.5. Discussion 2.6. References 2.7. Supplemental material 3. CHAPTER 2: Multi-Objective Land-Use Allocation Considering Landslide Risk under Climate Change: Case Study in Pyeongchang-gun, Korea 3.1. Introduction 3.2. Material and Methods 3.3. Results 3.4. Discussion 3.5. Conclusion 3.6. References 4. CHAPTER 3: Multi-Objective Planning Model for Urban Greening based on Optimization Algorithms 3.1. Introduction 3.2. Methods 3.3. Results 3.4. Discussion 3.5. Conclusion 3.6. References 3.7. Appendix 5. CONCLUSION REFERENCESDocto

    An Assessment of the Environmental Impacts of Urban Sprawl in Buffalo City Metropolitan Municipality, Eastern Cape Province

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    Large industrial and residential developments near towns and along highways associated with public policies have transformed the pattern of development over the recent years, creating a new urbanisation phenomenon; urban sprawl. Indiscriminate population densities, discontinuous and fragmented settlements, largely define urban sprawl. The progression of urban sprawl can be described by transformation in pattern over time, like proportional increase in built-up surface to population leading to rapid urban spatial expansion. Stemming an understanding from the processes, causes and patterns of urban sprawl, the consequences of sprawl on land and vegetation can be analysed. Environmental impacts to both the rural and urban population emanate from such instances, creating an excessive liability to the government. With attention to this and recognising the lack of discussion on the matter, the research deliberates some of the impacts observed in Buffalo City Metropolitan Municipality, Eastern Cape, South Africa. The study makes use of Geographic Information Systems and Remote Sensing with the assistance of landscape metrics. The influence of urban sprawl in this municipality has revealed impacts on vegetation, green areas and land in general. The results disclose that urban sprawl is a multidimensional phenomenon that is better explained using various methods (indices). Buffalo City Metropolitan municipality is located in Eastern Cape amidst the thicket ecosystem, the municipality has grown and expanded over the recent past. The study spread over an 18-year period from 1994- 2012. Based on field surveys and SPOT imagery, built-up areas of BCMM was extracted for different periods. Data used for the study are census data for BCMM, 1994, 2000, 2006 and 2012 SPOT images, images of BCMM acquired from Google earth 2018. The rate of transformation of the area was calculated and it was higher compared to that of population growth. Based on this data urban growth are analysed with the assistance of landscape metrics that include Shannon entropy. The outcomes confirm that this metropolitan municipality has experienced sprawl and sprawl has done so at cumulative rate

    Resilient Urban Futures

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    This open access book addresses the way in which urban and urbanizing regions profoundly impact and are impacted by climate change. The editors and authors show why cities must wage simultaneous battles to curb global climate change trends while adapting and transforming to address local climate impacts. This book addresses how cities develop anticipatory and long-range planning capacities for more resilient futures, earnest collaboration across disciplines, and radical reconfigurations of the power regimes that have institutionalized the disenfranchisement of minority groups. Although planning processes consider visions for the future, the editors highlight a more ambitious long-term positive visioning approach that accounts for unpredictability, system dynamics and equity in decision-making. This volume brings the science of urban transformation together with practices of professionals who govern and manage our social, ecological and technological systems to design processes by which cities may achieve resilient urban futures in the face of climate change

    Impacts of Landscape Change on Water Resources

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    Changes in land use and land cover can have many drivers, including population growth, urbanization, agriculture, demand for food, evolution of socio-economic structure, policy regulations, and climate variability. The impacts of these changes on water resources range from changes in water availability (due to changes in losses of water to evapotranspiration and recharge) to degradation of water quality (increased erosion, salinity, chemical loadings, and pathogens). The impacts are manifested through complex hydro-bio-geo-climate characteristics, which underscore the need for integrated scientific approaches to understand the impacts of landscape change on water resources. Several techniques, such as field studies, long-term monitoring, remote sensing technologies, and advanced modeling studies, have contributed to better understanding the modes and mechanisms by which landscape changes impact water resources. Such research studies can help unlock the complex interconnected influences of landscape on water resources in terms of quantity and quality at multiple spatial and temporal scales. In this Special Issue, we published a set of eight peer-reviewed articles elaborating on some of the specific topics of landscape changes and associated impacts on water resources

    Resilient Urban Futures

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    This open access book addresses the way in which urban and urbanizing regions profoundly impact and are impacted by climate change. The editors and authors show why cities must wage simultaneous battles to curb global climate change trends while adapting and transforming to address local climate impacts. This book addresses how cities develop anticipatory and long-range planning capacities for more resilient futures, earnest collaboration across disciplines, and radical reconfigurations of the power regimes that have institutionalized the disenfranchisement of minority groups. Although planning processes consider visions for the future, the editors highlight a more ambitious long-term positive visioning approach that accounts for unpredictability, system dynamics and equity in decision-making. This volume brings the science of urban transformation together with practices of professionals who govern and manage our social, ecological and technological systems to design processes by which cities may achieve resilient urban futures in the face of climate change

    Forecasting the response of Earth's surface to future climatic and land use changes: a review of methods and research needs

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    In the future, Earth will be warmer, precipitation events will be more extreme, global mean sea level will rise, and many arid and semiarid regions will be drier. Human modifications of landscapes will also occur at an accelerated rate as developed areas increase in size and population density. We now have gridded global forecasts, being continually improved, of the climatic and land use changes (C&LUC) that are likely to occur in the coming decades. However, besides a few exceptions, consensus forecasts do not exist for how these C&LUC will likely impact Earth-surface processes and hazards. In some cases, we have the tools to forecast the geomorphic responses to likely future C&LUC. Fully exploiting these models and utilizing these tools will require close collaboration among Earth-surface scientists and Earth-system modelers. This paper assesses the state-of-the-art tools and data that are being used or could be used to forecast changes in the state of Earth's surface as a result of likely future C&LUC. We also propose strategies for filling key knowledge gaps, emphasizing where additional basic research and/or collaboration across disciplines are necessary. The main body of the paper addresses cross-cutting issues, including the importance of nonlinear/threshold-dominated interactions among topography, vegetation, and sediment transport, as well as the importance of alternate stable states and extreme, rare events for understanding and forecasting Earth-surface response to C&LUC. Five supplements delve into different scales or process zones (global-scale assessments and fluvial, aeolian, glacial/periglacial, and coastal process zones) in detail
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