3,290 research outputs found

    Remote sensing of opium poppy cultivation in Afghanistan

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    This work investigates differences in the survey methodologies of the monitoring programmes of the United Nations Office on Drugs and Crime (UNODC) and the US Government that lead to discrepancies in quantitative information about poppy cultivation. The aim of the research is to improve annual estimates of opium production. Scientific trials conducted for the UK Government (2006โ€“2009) revealed differences between the two surveys that could account for the inconsistency in results. These related to the image interpretation of poppy from very high resolution satellite imagery, the mapping of the total area of agriculture and stratification using full coverage medium resolution imagery. MODIS time-series profiles of Normalised Difference Vegetation Index (NDVI), used to monitor Afghanistanโ€™s agricultural system, revealed significant variation in the agriculture area between years caused by land management practices and expansion into new areas. Image interpretation of crops was investigated as a source of bias within the sample using increasing levels of generalisation in sample interpretations. Automatic segmentation and object-based classification were tested as methods to improve consistency. Generalisation was found to bias final estimates of poppy up to 14%. Segments were consistent with manual field delineations but object-based classification caused a systematic labelling error. The findings show differences in survey estimates based on interpretation keys and the resolution of imagery, which is compounded in areas of marginal agriculture or years with poor crop establishment. Stratified and unstratified poppy cultivation estimates were made using buffered and unbuffered agricultural masks at resolutions of 20, 30 and 60 m, resampled from SPOT-5 10 m data. The number of strata (1, 4, 8, 13, 23, 40) and sample fraction (0.2 to 2%) used in the estimate were also investigated. Decreasing the resolution of the imagery and buffering increased unstratified estimates. Stratified estimates were more robust to changes in sample size and distribution. The mapping of the agricultural area explained differences in cultivation figures of the opium monitoring programmes in Afghanistan. Supporting methods for yield estimation for opium poppy were investigated at field sites in the UK in 2004, 2005 and 2010. Good empirical relationships were found between NDVI and the yield indicators of mature capsule volume and dry capsule yield. The results suggested a generalised relationship across all sampled fields and years (R2 >0.70) during the 3โ€“4 week period including poppy flowering. The application of this approach in Afghanistan was investigated using VHR satellite imagery and yield data from the UNODCโ€™s annual survey. Initial results indicated the potential of improved yield estimates using a smaller and targeted collection of ground observations as an alternative to random sampling. The recommendations for poppy cultivation surveys are: the use of image-based stratification for improved precision and reducing differences in the agricultural mask, and use of automatic segmentation for improved consistency in field delineation of poppy crops. The findings have wider implications for improved confidence in statistical estimates from remote sensing methodologies

    Assessing satellite-derived land product quality for earth system science applications: results from the ceos lpv sub-group

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    The value of satellite derived land products for science applications and research is dependent upon the known accuracy of the data. CEOS (Committee on Earth Observation Satellites), the space arm of the Group on Earth Observations (GEO), plays a key role in coordinating the land product validation process. The Land Product Validation (LPV) sub-group of the CEOS Working Group on Calibration and Validation (WGCV) aims to address the challenges associated with the validation of global land products. This paper provides an overview of LPV sub-group focus area activities, which cover seven terrestrial Essential Climate Variables (ECVs). The contribution will enhance coordination of the scientific needs of the Earth system communities with global LPV activities

    Time tracking of different cropping patterns using Landsat images under different agricultural systems during 1990-2050 in Cold China

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    Rapid cropland reclamation is underway in Cold China in response to increases in food demand, while the lack analyses of time series cropping pattern mappings limits our understanding of the acute transformation process of cropland structure and associated environmental effects. The Cold China contains different agricultural systems (state and private farming), and such systems could lead to different cropping patterns. So far, such changes have not been revealed yet. Based on the Landsat images, this study tracked cropping information in five-year increments (1990-1995, 1995-2000, 2000-2005, 2005-2010, and 2010-2015) and predicted future patterns for the period of 2020-2050 under different agricultural systems using developed method for determining cropland patterns. The following results were obtained: The available time series of Landsat images in Cold China met the requirements for long-term cropping pattern studies, and the developed method exhibited high accuracy (over 91%) and obtained precise spatial information. A new satellite evidence was observed that cropping patterns significantly differed between the two farm types, with paddy field in state farming expanding at a faster rate (from 2.66 to 68.56%) than those in private farming (from 10.12 to 34.98%). More than 70% of paddy expansion was attributed to the transformation of upland crop in each period at the pixel level, which led to a greater loss of upland crop in state farming than private farming (9505.66 km(2) vs. 2840.29 km(2)) during 1990-2015. Rapid cropland reclamation is projected to stagnate in 2020, while paddy expansion will continue until 2040 primarily in private farming in Cold China. This study provides new evidence for different land use change pattern mechanisms between different agricultural systems, and the results have significant implications for understanding and guiding agricultural system development

    ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„ ํ–ฅ์ƒ์„ ํ†ตํ•œ ์‹์ƒ ๋ณ€ํ™” ๋ชจ๋‹ˆํ„ฐ๋ง

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    ํ•™์œ„๋…ผ๋ฌธ(๋ฐ•์‚ฌ) -- ์„œ์šธ๋Œ€ํ•™๊ต๋Œ€ํ•™์› : ํ™˜๊ฒฝ๋Œ€ํ•™์› ํ˜‘๋™๊ณผ์ • ์กฐ๊ฒฝํ•™, 2023. 2. ๋ฅ˜์˜๋ ฌ.์œก์ƒ ์ƒํƒœ๊ณ„์—์„œ ๋Œ€๊ธฐ๊ถŒ๊ณผ ์ƒ๋ฌผ๊ถŒ์˜ ์ƒํ˜ธ ์ž‘์šฉ์„ ์ดํ•ดํ•˜๊ธฐ ์œ„ํ•ด์„œ๋Š” ์‹์ƒ ๋ณ€ํ™”์˜ ๋ชจ๋‹ˆํ„ฐ๋ง์ด ํ•„์š”ํ•˜๋‹ค. ์ด ๋•Œ, ์œ„์„ฑ์˜์ƒ์€ ์ง€ํ‘œ๋ฉด์„ ๊ด€์ธกํ•˜์—ฌ ์‹์ƒ์ง€๋„๋ฅผ ์ œ๊ณตํ•  ์ˆ˜ ์žˆ์ง€๋งŒ, ์ง€ํ‘œ๋ณ€ํ™”์˜ ์ƒ์„ธํ•œ ์ •๋ณด๋Š” ๊ตฌ๋ฆ„์ด๋‚˜ ์œ„์„ฑ ์ด๋ฏธ์ง€์˜ ๊ณต๊ฐ„ ํ•ด์ƒ๋„์— ์˜ํ•ด ์ œํ•œ๋˜์—ˆ๋‹ค. ๋˜ํ•œ ์œ„์„ฑ์˜์ƒ์˜ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๊ฐ€ ์‹์ƒ์ง€๋„๋ฅผ ํ†ตํ•œ ๊ด‘ํ•ฉ์„ฑ ๋ชจ๋‹ˆํ„ฐ๋ง์— ๋ฏธ์น˜๋Š” ์˜ํ–ฅ์€ ์™„์ „ํžˆ ๋ฐํ˜€์ง€์ง€ ์•Š์•˜๋‹ค. ๋ณธ ๋…ผ๋ฌธ์—์„œ๋Š” ๊ณ ํ•ด์ƒ๋„ ์‹์ƒ ์ง€๋„๋ฅผ ์ผ๋‹จ์œ„๋กœ ์ƒ์„ฑํ•˜๊ธฐ ์œ„์„ฑ ์˜์ƒ์˜ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋ฅผ ํ–ฅ์ƒ์‹œํ‚ค๋Š” ๊ฒƒ์„ ๋ชฉํ‘œ๋กœ ํ•˜์˜€๋‹ค. ๊ณ ํ•ด์ƒ๋„ ์œ„์„ฑ์˜์ƒ์„ ํ™œ์šฉํ•œ ์‹์ƒ ๋ณ€ํ™” ๋ชจ๋‹ˆํ„ฐ๋ง์„ ์‹œ๊ณต๊ฐ„์ ์œผ๋กœ ํ™•์žฅํ•˜๊ธฐ ์œ„ํ•ด 1) ์ •์ง€๊ถค๋„ ์œ„์„ฑ์„ ํ™œ์šฉํ•œ ์˜์ƒ์œตํ•ฉ์„ ํ†ตํ•ด ์‹œ๊ฐ„ํ•ด์ƒ๋„ ํ–ฅ์ƒ, 2) ์ ๋Œ€์ ์ƒ์„ฑ๋„คํŠธ์›Œํฌ๋ฅผ ํ™œ์šฉํ•œ ๊ณต๊ฐ„ํ•ด์ƒ๋„ ํ–ฅ์ƒ, 3) ์‹œ๊ณต๊ฐ„ํ•ด์ƒ๋„๊ฐ€ ๋†’์€ ์œ„์„ฑ์˜์ƒ์„ ํ† ์ง€ํ”ผ๋ณต์ด ๊ท ์งˆํ•˜์ง€ ์•Š์€ ๊ณต๊ฐ„์—์„œ ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ ๋ชจ๋‹ˆํ„ฐ๋ง์„ ์ˆ˜ํ–‰ํ•˜์˜€๋‹ค. ์ด์ฒ˜๋Ÿผ, ์œ„์„ฑ๊ธฐ๋ฐ˜ ์›๊ฒฉํƒ์ง€์—์„œ ์ƒˆ๋กœ์šด ๊ธฐ์ˆ ์ด ๋“ฑ์žฅํ•จ์— ๋”ฐ๋ผ ํ˜„์žฌ ๋ฐ ๊ณผ๊ฑฐ์˜ ์œ„์„ฑ์˜์ƒ์€ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„ ์ธก๋ฉด์—์„œ ํ–ฅ์ƒ๋˜์–ด ์‹์ƒ ๋ณ€ํ™”์˜ ๋ชจ๋‹ˆํ„ฐ๋ง ํ•  ์ˆ˜ ์žˆ๋‹ค. ์ œ2์žฅ์—์„œ๋Š” ์ •์ง€๊ถค๋„์œ„์„ฑ์˜์ƒ์„ ํ™œ์šฉํ•˜๋Š” ์‹œ๊ณต๊ฐ„ ์˜์ƒ์œตํ•ฉ์œผ๋กœ ์‹๋ฌผ์˜ ๊ด‘ํ•ฉ์„ฑ์„ ๋ชจ๋‹ˆํ„ฐ๋ง ํ–ˆ์„ ๋•Œ, ์‹œ๊ฐ„ํ•ด์ƒ๋„๊ฐ€ ํ–ฅ์ƒ๋จ์„ ๋ณด์˜€๋‹ค. ์‹œ๊ณต๊ฐ„ ์˜์ƒ์œตํ•ฉ ์‹œ, ๊ตฌ๋ฆ„ํƒ์ง€, ์–‘๋ฐฉํ–ฅ ๋ฐ˜์‚ฌ ํ•จ์ˆ˜ ์กฐ์ •, ๊ณต๊ฐ„ ๋“ฑ๋ก, ์‹œ๊ณต๊ฐ„ ์œตํ•ฉ, ์‹œ๊ณต๊ฐ„ ๊ฒฐ์ธก์น˜ ๋ณด์™„ ๋“ฑ์˜ ๊ณผ์ •์„ ๊ฑฐ์นœ๋‹ค. ์ด ์˜์ƒ์œตํ•ฉ ์‚ฐ์ถœ๋ฌผ์€ ๊ฒฝ์ž‘๊ด€๋ฆฌ ๋“ฑ์œผ๋กœ ์‹์ƒ ์ง€์ˆ˜์˜ ์—ฐ๊ฐ„ ๋ณ€๋™์ด ํฐ ๋‘ ์žฅ์†Œ(๋†๊ฒฝ์ง€์™€ ๋‚™์—ฝ์ˆ˜๋ฆผ)์—์„œ ํ‰๊ฐ€ํ•˜์˜€๋‹ค. ๊ทธ ๊ฒฐ๊ณผ, ์‹œ๊ณต๊ฐ„ ์˜์ƒ์œตํ•ฉ ์‚ฐ์ถœ๋ฌผ์€ ๊ฒฐ์ธก์น˜ ์—†์ด ํ˜„์žฅ๊ด€์ธก์„ ์˜ˆ์ธกํ•˜์˜€๋‹ค (R2 = 0.71, ์ƒ๋Œ€ ํŽธํ–ฅ = 5.64% ๋†๊ฒฝ์ง€; R2 = 0.79, ์ƒ๋Œ€ ํŽธํ–ฅ = -13.8%, ํ™œ์—ฝ์ˆ˜๋ฆผ). ์‹œ๊ณต๊ฐ„ ์˜์ƒ์œตํ•ฉ์€ ์‹์ƒ ์ง€๋„์˜ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋ฅผ ์ ์ง„์ ์œผ๋กœ ๊ฐœ์„ ํ•˜์—ฌ, ์‹๋ฌผ ์ƒ์žฅ๊ธฐ๋™์•ˆ ์œ„์„ฑ์˜์ƒ์ด ํ˜„์žฅ ๊ด€์ธก์„ ๊ณผ์†Œ ํ‰๊ฐ€๋ฅผ ์ค„์˜€๋‹ค. ์˜์ƒ์œตํ•ฉ์€ ๋†’์€ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋กœ ๊ด‘ํ•ฉ์„ฑ ์ง€๋„๋ฅผ ์ผ๊ฐ„๊ฒฉ์œผ๋กœ ์ƒ์„ฑํ•˜๊ธฐ์— ์ด๋ฅผ ํ™œ์šฉํ•˜์—ฌ ์œ„์„ฑ ์˜์ƒ์˜ ์ œํ•œ๋œ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋กœ ๋ฐํ˜€์ง€์ง€ ์•Š์€ ์‹๋ฌผ๋ณ€ํ™”์˜ ๊ณผ์ •์„ ๋ฐœ๊ฒฌํ•˜๊ธธ ๊ธฐ๋Œ€ํ•œ๋‹ค. ์‹์ƒ์˜ ๊ณต๊ฐ„๋ถ„ํฌ์€ ์ •๋ฐ€๋†์—…๊ณผ ํ† ์ง€ ํ”ผ๋ณต ๋ณ€ํ™” ๋ชจ๋‹ˆํ„ฐ๋ง์„ ์œ„ํ•ด ํ•„์ˆ˜์ ์ด๋‹ค. ๊ณ ํ•ด์ƒ๋„ ์œ„์„ฑ์˜์ƒ์œผ๋กœ ์ง€๊ตฌ ํ‘œ๋ฉด์„ ๊ด€์ธกํ•˜๋Š” ๊ฒƒ์„ ์šฉ์ดํ•˜๊ฒŒ ํ•ด์กŒ๋‹ค. ํŠนํžˆ Planet Fusion์€ ์ดˆ์†Œํ˜•์œ„์„ฑ๊ตฐ ๋ฐ์ดํ„ฐ๋ฅผ ์ตœ๋Œ€ํ•œ ํ™œ์šฉํ•ด ๋ฐ์ดํ„ฐ ๊ฒฐ์ธก์ด ์—†๋Š” 3m ๊ณต๊ฐ„ ํ•ด์ƒ๋„์˜ ์ง€ํ‘œ ํ‘œ๋ฉด ๋ฐ˜์‚ฌ๋„์ด๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ๊ณผ๊ฑฐ ์œ„์„ฑ ์„ผ์„œ(Landsat์˜ ๊ฒฝ์šฐ 30~60m)์˜ ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋Š” ์‹์ƒ์˜ ๊ณต๊ฐ„์  ๋ณ€ํ™”๋ฅผ ์ƒ์„ธ ๋ถ„์„ํ•˜๋Š” ๊ฒƒ์„ ์ œํ•œํ–ˆ๋‹ค. ์ œ3์žฅ์—์„œ๋Š” Landsat ๋ฐ์ดํ„ฐ์˜ ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋ฅผ ํ–ฅ์ƒํ•˜๊ธฐ ์œ„ํ•ด Planet Fusion ๋ฐ Landsat 8 ๋ฐ์ดํ„ฐ๋ฅผ ์‚ฌ์šฉํ•˜์—ฌ ์ด์ค‘ ์ ๋Œ€์  ์ƒ์„ฑ ๋„คํŠธ์›Œํฌ(the dual RSS-GAN)๋ฅผ ํ•™์Šต์‹œ์ผœ, ๊ณ ํ•ด์ƒ๋„ ์ •๊ทœํ™” ์‹์ƒ ์ง€์ˆ˜(NDVI)์™€ ์‹๋ฌผ ๊ทผ์ ์™ธ์„  ๋ฐ˜์‚ฌ(NIRv)๋„๋ฅผ ์ƒ์„ฑํ•˜๋Š” ํ•œ๋‹ค. ํƒ€์›Œ๊ธฐ๋ฐ˜ ํ˜„์žฅ ์‹์ƒ์ง€์ˆ˜(์ตœ๋Œ€ 8๋…„)์™€ ๋“œ๋ก ๊ธฐ๋ฐ˜ ์ดˆ๋ถ„๊ด‘์ง€๋„๋กœ the dual RSS-GAN์˜ ์„ฑ๋Šฅ์„ ๋Œ€ํ•œ๋ฏผ๊ตญ ๋‚ด ๋‘ ๋Œ€์ƒ์ง€(๋†๊ฒฝ์ง€์™€ ํ™œ์—ฝ์ˆ˜๋ฆผ)์—์„œ ํ‰๊ฐ€ํ–ˆ๋‹ค. The dual RSS-GAN์€ Landsat 8 ์˜์ƒ์˜ ๊ณต๊ฐ„ํ•ด์ƒ๋„๋ฅผ ํ–ฅ์ƒ์‹œ์ผœ ๊ณต๊ฐ„ ํ‘œํ˜„์„ ๋ณด์™„ํ•˜๊ณ  ์‹์ƒ ์ง€์ˆ˜์˜ ๊ณ„์ ˆ์  ๋ณ€ํ™”๋ฅผ ํฌ์ฐฉํ–ˆ๋‹ค(R2> 0.96). ๊ทธ๋ฆฌ๊ณ  the dual RSS-GAN์€ Landsat 8 ์‹์ƒ ์ง€์ˆ˜๊ฐ€ ํ˜„์žฅ์— ๋น„ํ•ด ๊ณผ์†Œ ํ‰๊ฐ€๋˜๋Š” ๊ฒƒ์„ ์™„ํ™”ํ–ˆ๋‹ค. ํ˜„์žฅ ๊ด€์ธก์— ๋น„ํ•ด ์ด์ค‘ RSS-GAN๊ณผ Landsat 8์˜ ์ƒ๋Œ€ ํŽธํ–ฅ ๊ฐ’ ๊ฐ๊ฐ -0.8% ์—์„œ -1.5%, -10.3% ์—์„œ -4.6% ์˜€๋‹ค. ์ด๋Ÿฌํ•œ ๊ฐœ์„ ์€ Planet Fusion์˜ ๊ณต๊ฐ„์ •๋ณด๋ฅผ ์ด์ค‘ RSS-GAN๋กœ ํ•™์Šตํ•˜์˜€๊ธฐ์— ๊ฐ€๋Šฅํ–ˆ๋‹ค. ํ—ค๋‹น ์—ฐ๊ตฌ ๊ฒฐ๊ณผ๋Š” Landsat ์˜์ƒ์˜ ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋ฅผ ํ–ฅ์ƒ์‹œ์ผœ ์ˆจ๊ฒจ์ง„ ๊ณต๊ฐ„ ์ •๋ณด๋ฅผ ์ œ๊ณตํ•˜๋Š” ์ƒˆ๋กœ์šด ์ ‘๊ทผ ๋ฐฉ์‹์ด๋‹ค. ๊ณ ํ•ด์ƒ๋„์—์„œ ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ ์ง€๋„๋Š” ํ† ์ง€ํ”ผ๋ณต์ด ๋ณต์žกํ•œ ๊ณต๊ฐ„์—์„œ ํƒ„์†Œ ์ˆœํ™˜ ๋ชจ๋‹ˆํ„ฐ๋ง์‹œ ํ•„์ˆ˜์ ์ด๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ Sentinel-2, Landsat ๋ฐ MODIS์™€ ๊ฐ™์ด ํƒœ์–‘ ๋™์กฐ ๊ถค๋„์— ์žˆ๋Š” ์œ„์„ฑ์€ ๊ณต๊ฐ„ ํ•ด์ƒ๋„๊ฐ€ ๋†’๊ฑฐ๋‚˜ ์‹œ๊ฐ„ ํ•ด์ƒ๋„ ๋†’์€ ์œ„์„ฑ์˜์ƒ๋งŒ ์ œ๊ณตํ•  ์ˆ˜ ์žˆ๋‹ค. ์ตœ๊ทผ ๋ฐœ์‚ฌ๋œ ์ดˆ์†Œํ˜•์œ„์„ฑ๊ตฐ์€ ์ด๋Ÿฌํ•œ ํ•ด์ƒ๋„ ํ•œ๊ณ„์„ ๊ทน๋ณตํ•  ์ˆ˜ ์žˆ๋‹ค. ํŠนํžˆ Planet Fusion์€ ์ดˆ์†Œํ˜•์œ„์„ฑ ์ž๋ฃŒ์˜ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋กœ ์ง€ํ‘œ๋ฉด์„ ๊ด€์ธกํ•  ์ˆ˜ ์žˆ๋‹ค. 4์žฅ์—์„œ, Planet Fusion ์ง€ํ‘œ๋ฐ˜์‚ฌ๋„๋ฅผ ์ด์šฉํ•˜์—ฌ ์‹์ƒ์—์„œ ๋ฐ˜์‚ฌ๋œ ๊ทผ์ ์™ธ์„  ๋ณต์‚ฌ(NIRvP)๋ฅผ 3m ํ•ด์ƒ๋„ ์ง€๋„๋ฅผ ์ผ๊ฐ„๊ฒฉ์œผ๋กœ ์ƒ์„ฑํ–ˆ๋‹ค. ๊ทธ๋Ÿฐ ๋‹ค์Œ ๋ฏธ๊ตญ ์บ˜๋ฆฌํฌ๋‹ˆ์•„์ฃผ ์ƒˆํฌ๋ผ๋ฉ˜ํ† -์ƒŒ ํ˜ธ์•„ํ‚จ ๋ธํƒ€์˜ ํ”Œ๋Ÿญ์Šค ํƒ€์›Œ ๋„คํŠธ์›Œํฌ ๋ฐ์ดํ„ฐ์™€ ๋น„๊ตํ•˜์—ฌ ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ์„ ์ถ”์ •ํ•˜๊ธฐ ์œ„ํ•œ NIRvP ์ง€๋„์˜ ์„ฑ๋Šฅ์„ ํ‰๊ฐ€ํ•˜์˜€๋‹ค. ์ „์ฒด์ ์œผ๋กœ NIRvP ์ง€๋„๋Š” ์Šต์ง€์˜ ์žฆ์€ ์ˆ˜์œ„ ๋ณ€ํ™”์—๋„ ๋ถˆ๊ตฌํ•˜๊ณ  ๊ฐœ๋ณ„ ๋Œ€์ƒ์ง€์˜ ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ์˜ ์‹œ๊ฐ„์  ๋ณ€ํ™”๋ฅผ ํฌ์ฐฉํ•˜์˜€๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ๋Œ€์ƒ์ง€ ์ „์ฒด์— ๋Œ€ํ•œ NIRvP ์ง€๋„์™€ ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ ์‚ฌ์ด์˜ ๊ด€๊ณ„๋Š” NIRvP ์ง€๋„๋ฅผ ํ”Œ๋Ÿญ์Šค ํƒ€์›Œ ๊ด€์ธก๋ฒ”์œ„์™€ ์ผ์น˜์‹œํ‚ฌ ๋•Œ๋งŒ ๋†’์€ ์ƒ๊ด€๊ด€๊ณ„๋ฅผ ๋ณด์˜€๋‹ค. ๊ด€์ธก๋ฒ”์œ„๋ฅผ ์ผ์น˜์‹œํ‚ฌ ๊ฒฝ์šฐ, NIRvP ์ง€๋„๋Š” ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ์„ ์ถ”์ •ํ•˜๋Š” ๋ฐ ์žˆ์–ด ํ˜„์žฅ NIRvP๋ณด๋‹ค ์šฐ์ˆ˜ํ•œ ์„ฑ๋Šฅ์„ ๋ณด์˜€๋‹ค. ์ด๋Ÿฌํ•œ ์„ฑ๋Šฅ ์ฐจ์ด๋Š” ํ”Œ๋Ÿญ์Šค ํƒ€์›Œ ๊ด€์ธก๋ฒ”์œ„๋ฅผ ์ผ์น˜์‹œํ‚ฌ ๋•Œ, ์—ฐ๊ตฌ ๋Œ€์ƒ์ง€ ๊ฐ„์˜ NIRvP-์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ ๊ด€๊ณ„์˜ ๊ธฐ์šธ๊ธฐ๊ฐ€ ์ผ๊ด€์„ฑ์„ ๋ณด์˜€๊ธฐ ๋•Œ๋ฌธ์ด๋‹ค. ๋ณธ ์—ฐ๊ตฌ ๊ฒฐ๊ณผ๋Š” ์œ„์„ฑ ๊ด€์ธก์„ ํ”Œ๋Ÿญ์Šค ํƒ€์›Œ ๊ด€์ธก๋ฒ”์œ„์™€ ์ผ์น˜์‹œํ‚ค๋Š” ๊ฒƒ์˜ ์ค‘์š”์„ฑ์„ ๋ณด์—ฌ์ฃผ๊ณ  ๋†’์€ ์‹œ๊ณต๊ฐ„ ํ•ด์ƒ๋„๋กœ ์‹๋ฌผ ๊ด‘ํ•ฉ์„ฑ์„ ์›๊ฒฉ์œผ๋กœ ๋ชจ๋‹ˆํ„ฐ๋งํ•˜๋Š” ์ดˆ์†Œํ˜•์œ„์„ฑ๊ตฐ ์ž๋ฃŒ์˜ ์ž ์žฌ๋ ฅ์„ ๋ณด์—ฌ์ค€๋‹ค.Monitoring changes in terrestrial vegetation is essential to understanding interactions between atmosphere and biosphere, especially terrestrial ecosystem. To this end, satellite remote sensing offer maps for examining land surface in different scales. However, the detailed information was hindered under the clouds or limited by the spatial resolution of satellite imagery. Moreover, the impacts of spatial and temporal resolution in photosynthesis monitoring were not fully revealed. In this dissertation, I aimed to enhance the spatial and temporal resolution of satellite imagery towards daily gap-free vegetation maps with high spatial resolution. In order to expand vegetation change monitoring in time and space using high-resolution satellite images, I 1) improved temporal resolution of satellite dataset through image fusion using geostationary satellites, 2) improved spatial resolution of satellite dataset using generative adversarial networks, and 3) showed the use of high spatiotemporal resolution maps for monitoring plant photosynthesis especially over heterogeneous landscapes. With the advent of new techniques in satellite remote sensing, current and past datasets can be fully utilized for monitoring vegetation changes in the respect of spatial and temporal resolution. In Chapter 2, I developed the integrated system that implemented geostationary satellite products in the spatiotemporal image fusion method for monitoring canopy photosynthesis. The integrated system contains the series of process (i.e., cloud masking, nadir bidirectional reflectance function adjustment, spatial registration, spatiotemporal image fusion, spatial gap-filling, temporal-gap-filling). I conducted the evaluation of the integrated system over heterogeneous rice paddy landscape where the drastic land cover changes were caused by cultivation management and deciduous forest where consecutive changes occurred in time. The results showed that the integrated system well predict in situ measurements without data gaps (R2 = 0.71, relative bias = 5.64% at rice paddy site; R2 = 0.79, relative bias = -13.8% at deciduous forest site). The integrated system gradually improved the spatiotemporal resolution of vegetation maps, reducing the underestimation of in situ measurements, especially during peak growing season. Since the integrated system generates daily canopy photosynthesis maps for monitoring dynamics among regions of interest worldwide with high spatial resolution. I anticipate future efforts to reveal the hindered information by the limited spatial and temporal resolution of satellite imagery. Detailed spatial representations of terrestrial vegetation are essential for precision agricultural applications and the monitoring of land cover changes in heterogeneous landscapes. The advent of satellite-based remote sensing has facilitated daily observations of the Earths surface with high spatial resolution. In particular, a data fusion product such as Planet Fusion has realized the delivery of daily, gap-free surface reflectance data with 3-m pixel resolution through full utilization of relatively recent (i.e., 2018-) CubeSat constellation data. However, the spatial resolution of past satellite sensors (i.e., 30โ€“60 m for Landsat) has restricted the detailed spatial analysis of past changes in vegetation. In Chapter 3, to overcome the spatial resolution constraint of Landsat data for long-term vegetation monitoring, we propose a dual remote-sensing super-resolution generative adversarial network (dual RSS-GAN) combining Planet Fusion and Landsat 8 data to simulate spatially enhanced long-term time-series of the normalized difference vegetation index (NDVI) and near-infrared reflectance from vegetation (NIRv). We evaluated the performance of the dual RSS-GAN against in situ tower-based continuous measurements (up to 8 years) and remotely piloted aerial system-based maps of cropland and deciduous forest in the Republic of Korea. The dual RSS-GAN enhanced spatial representations in Landsat 8 images and captured seasonal variation in vegetation indices (R2 > 0.95, for the dual RSS-GAN maps vs. in situ data from all sites). Overall, the dual RSS-GAN reduced Landsat 8 vegetation index underestimations compared with in situ measurements; relative bias values of NDVI ranged from โˆ’3.2% to 1.2% and โˆ’12.4% to โˆ’3.7% for the dual RSS-GAN and Landsat 8, respectively. This improvement was caused by spatial enhancement through the dual RSS-GAN, which captured fine-scale information from Planet Fusion. This study presents a new approach for the restoration of hidden sub-pixel spatial information in Landsat images. Mapping canopy photosynthesis in both high spatial and temporal resolution is essential for carbon cycle monitoring in heterogeneous areas. However, well established satellites in sun-synchronous orbits such as Sentinel-2, Landsat and MODIS can only provide either high spatial or high temporal resolution but not both. Recently established CubeSat satellite constellations have created an opportunity to overcome this resolution trade-off. In particular, Planet Fusion allows full utilization of the CubeSat data resolution and coverage while maintaining high radiometric quality. In Chapter 4, I used the Planet Fusion surface reflectance product to calculate daily, 3-m resolution, gap-free maps of the near-infrared radiation reflected from vegetation (NIRvP). I then evaluated the performance of these NIRvP maps for estimating canopy photosynthesis by comparing with data from a flux tower network in Sacramento-San Joaquin Delta, California, USA. Overall, NIRvP maps captured temporal variations in canopy photosynthesis of individual sites, despite changes in water extent in the wetlands and frequent mowing in the crop fields. When combining data from all sites, however, I found that robust agreement between NIRvP maps and canopy photosynthesis could only be achieved when matching NIRvP maps to the flux tower footprints. In this case of matched footprints, NIRvP maps showed considerably better performance than in situ NIRvP in estimating canopy photosynthesis both for daily sum and data around the time of satellite overpass (R2 = 0.78 vs. 0.60, for maps vs. in situ for the satellite overpass time case). This difference in performance was mostly due to the higher degree of consistency in slopes of NIRvP-canopy photosynthesis relationships across the study sites for flux tower footprint-matched maps. Our results show the importance of matching satellite observations to the flux tower footprint and demonstrate the potential of CubeSat constellation imagery to monitor canopy photosynthesis remotely at high spatio-temporal resolution.Chapter 1. Introduction 2 1. Background 2 1.1 Daily gap-free surface reflectance using geostationary satellite products 2 1.2 Monitoring past vegetation changes with high-spatial-resolution 3 1.3 High spatiotemporal resolution vegetation photosynthesis maps 4 2. Purpose of Research 4 Chapter 2. Generating daily gap-filled BRDF adjusted surface reflectance product at 10 m resolution using geostationary satellite product for monitoring daily canopy photosynthesis 6 1. Introduction 6 2. Methods 11 2.1 Study sites 11 2.2 In situ measurements 13 2.3 Satellite products 14 2.4 Integrated system 17 2.5 Canopy photosynthesis 21 2.6 Evaluation 23 3. Results and discussion 24 3.1 Comparison of STIF NDVI and NIRv with in situ NDVI and NIRv 24 3.2 Comparison of STIF NIRvP with in situ NIRvP 28 4. Conclusion 31 Chapter 3. Super-resolution of historic Landsat imagery using a dual Generative Adversarial Network (GAN) model with CubeSat constellation imagery for monitoring vegetation changes 32 1. Introduction 32 2. Methods 38 2.1 Real-ESRGAN model 38 2.2 Study sites 40 2.3 In situ measurements 42 2.4 Vegetation index 44 2.5 Satellite data 45 2.6 Planet Fusion 48 2.7 Dual RSS-GAN via fine-tuned Real-ESRGAN 49 2.8 Evaluation 54 3. Results 57 3.1 Comparison of NDVI and NIRv maps from Planet Fusion, Sentinel 2 NBAR, and Landsat 8 NBAR data with in situ NDVI and NIRv 57 3.2 Comparison of dual RSS-SRGAN model results with Landsat 8 NDVI and NIRv 60 3.3 Comparison of dual RSS-GAN model results with respect to in situ time-series NDVI and NIRv 63 3.4 Comparison of the dual RSS-GAN model with NDVI and NIRv maps derived from RPAS 66 4. Discussion 70 4.1 Monitoring changes in terrestrial vegetation using the dual RSS-GAN model 70 4.2 CubeSat data in the dual RSS-GAN model 72 4.3 Perspectives and limitations 73 5. Conclusion 78 Appendices 79 Supplementary material 82 Chapter 4. Matching high resolution satellite data and flux tower footprints improves their agreement in photosynthesis estimates 85 1. Introduction 85 2. Methods 89 2.1 Study sites 89 2.2 In situ measurements 92 2.3 Planet Fusion NIRvP 94 2.4 Flux footprint model 98 2.5 Evaluation 98 3. Results 105 3.1 Comparison of Planet Fusion NIRv and NIRvP with in situ NIRv and NIRvP 105 3.2 Comparison of instantaneous Planet Fusion NIRv and NIRvP with against tower GPP estimates 108 3.3 Daily GPP estimation from Planet Fusion -derived NIRvP 114 4. Discussion 118 4.1 Flux tower footprint matching and effects of spatial and temporal resolution on GPP estimation 118 4.2 Roles of radiation component in GPP mapping 123 4.3 Limitations and perspectives 126 5. Conclusion 133 Appendix 135 Supplementary Materials 144 Chapter 5. Conclusion 153 Bibliography 155 Abstract in Korea 199 Acknowledgements 202๋ฐ•

    Assessing the role of EO in biodiversity monitoring: options for integrating in-situ observations with EO within the context of the EBONE concept

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    The European Biodiversity Observation Network (EBONE) is a European contribution on terrestrial monitoring to GEO BON, the Group on Earth Observations Biodiversity Observation Network. EBONEโ€™s aims are to develop a system of biodiversity observation at regional, national and European levels by assessing existing approaches in terms of their validity and applicability starting in Europe, then expanding to regions in Africa. The objective of EBONE is to deliver: 1. A sound scientific basis for the production of statistical estimates of stock and change of key indicators; 2. The development of a system for estimating past changes and forecasting and testing policy options and management strategies for threatened ecosystems and species; 3. A proposal for a cost-effective biodiversity monitoring system. There is a consensus that Earth Observation (EO) has a role to play in monitoring biodiversity. With its capacity to observe detailed spatial patterns and variability across large areas at regular intervals, our instinct suggests that EO could deliver the type of spatial and temporal coverage that is beyond reach with in-situ efforts. Furthermore, when considering the emerging networks of in-situ observations, the prospect of enhancing the quality of the information whilst reducing cost through integration is compelling. This report gives a realistic assessment of the role of EO in biodiversity monitoring and the options for integrating in-situ observations with EO within the context of the EBONE concept (cfr. EBONE-ID1.4). The assessment is mainly based on a set of targeted pilot studies. Building on this assessment, the report then presents a series of recommendations on the best options for using EO in an effective, consistent and sustainable biodiversity monitoring scheme. The issues that we faced were many: 1. Integration can be interpreted in different ways. One possible interpretation is: the combined use of independent data sets to deliver a different but improved data set; another is: the use of one data set to complement another dataset. 2. The targeted improvement will vary with stakeholder group: some will seek for more efficiency, others for more reliable estimates (accuracy and/or precision); others for more detail in space and/or time or more of everything. 3. Integration requires a link between the datasets (EO and in-situ). The strength of the link between reflected electromagnetic radiation and the habitats and their biodiversity observed in-situ is function of many variables, for example: the spatial scale of the observations; timing of the observations; the adopted nomenclature for classification; the complexity of the landscape in terms of composition, spatial structure and the physical environment; the habitat and land cover types under consideration. 4. The type of the EO data available varies (function of e.g. budget, size and location of region, cloudiness, national and/or international investment in airborne campaigns or space technology) which determines its capability to deliver the required output. EO and in-situ could be combined in different ways, depending on the type of integration we wanted to achieve and the targeted improvement. We aimed for an improvement in accuracy (i.e. the reduction in error of our indicator estimate calculated for an environmental zone). Furthermore, EO would also provide the spatial patterns for correlated in-situ data. EBONE in its initial development, focused on three main indicators covering: (i) the extent and change of habitats of European interest in the context of a general habitat assessment; (ii) abundance and distribution of selected species (birds, butterflies and plants); and (iii) fragmentation of natural and semi-natural areas. For habitat extent, we decided that it did not matter how in-situ was integrated with EO as long as we could demonstrate that acceptable accuracies could be achieved and the precision could consistently be improved. The nomenclature used to map habitats in-situ was the General Habitat Classification. We considered the following options where the EO and in-situ play different roles: using in-situ samples to re-calibrate a habitat map independently derived from EO; improving the accuracy of in-situ sampled habitat statistics, by post-stratification with correlated EO data; and using in-situ samples to train the classification of EO data into habitat types where the EO data delivers full coverage or a larger number of samples. For some of the above cases we also considered the impact that the sampling strategy employed to deliver the samples would have on the accuracy and precision achieved. Restricted access to European wide species data prevented work on the indicator โ€˜abundance and distribution of speciesโ€™. With respect to the indicator โ€˜fragmentationโ€™, we investigated ways of delivering EO derived measures of habitat patterns that are meaningful to sampled in-situ observations

    Vicarious Methodologies to Assess and Improve the Quality of the Optical Remote Sensing Images: A Critical Review

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    Over the past decade, number of optical Earth observing satellites performing remote sensing has increased substantially, dramatically increasing the capability to monitor the Earth. The quantity of remote sensing satellite increase is primarily driven by improved technology, miniaturization of components, reduced manufacturing, and launch cost. These satellites often lack on-board calibrators that a large satellite utilizes to ensure high quality (e.g., radiometric, geometric, spatial quality, etc.) scientific measurement. To address this issue, this work presents โ€œbestโ€ vicarious image quality assessment and improvement techniques for those kinds of optical satellites which lacks on-board calibration system. In this article, image quality categories have been explored, and essential quality parameters (e.g., absolute and relative calibration, aliasing, etc.) have been identified. For each of the parameters, appropriate characterization methods are identified along with its specifications or requirements. In cases of multiple methods, recommendation has been made based-on the strengths and weaknesses of each method. Furthermore, processing steps have been presented, including examples. Essentially, this paper provides a comprehensive study of the criteria that needs to be assessed to evaluate remote sensing satellite data quality, and best vicarious methodologies to evaluate identified quality parameters such as coherent noise, ground sample distance, etc

    ๋“œ๋ก ์„ ํ™œ์šฉํ•œ ์œ„์„ฑ ์ง€ํ‘œ๋ฐ˜์‚ฌ๋„ ์‚ฐ์ถœ๋ฌผ ๊ณต๊ฐ„ ํŒจํ„ด ๋ถ„์„

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    ํ•™์œ„๋…ผ๋ฌธ(์„์‚ฌ) -- ์„œ์šธ๋Œ€ํ•™๊ต๋Œ€ํ•™์› : ๋†์—…์ƒ๋ช…๊ณผํ•™๋Œ€ํ•™ ์ƒํƒœ์กฐ๊ฒฝยท์ง€์—ญ์‹œ์Šคํ…œ๊ณตํ•™๋ถ€(์ƒํƒœ์กฐ๊ฒฝํ•™), 2021.8. ์กฐ๋Œ€์†”.High-resolution satellites are assigned to monitor land surface in detail. The reliable surface reflectance (SR) is the fundamental in terrestrial ecosystem modeling so the temporal and spatial validation is essential. Usually based on multiple ground control points (GCPs), field spectroscopy guarantees the temporal continuity. Due to limited sampling, however, it hardly illustrates the spatial pattern. As a map, the pixelwise spatial variability of SR products is not well-documented. In this study, we introduced drone-based hyperspectral image (HSI) as a reference and compared the map with Sentinel 2 and Landsat 8 SR products on a heterogeneous rice paddy landscape. First, HSI was validated by field spectroscopy and swath overlapping, which assured qualitative radiometric accuracy within the viewing geometry. Second, HSI was matched to the satellite SRs. It involves spectral and spatial aggregation, co-registration and nadir bidirectional reflectance distribution function (BRDF)-adjusted reflectance (NBAR) conversion. Then, we 1) quantified the spatial variability of the satellite SRs and the vegetation indices (VIs) including NDVI and NIRv by APU matrix, 2) qualified them pixelwise by theoretical error budget and 3) examined the improvement by BRDF normalization. Sentinel 2 SR exhibits overall good agreement with drone HSI while the two NIRs are biased up to 10%. Despite the bias in NIR, the NDVI shows a good match on vegetated areas and the NIRv only displays the discrepancy on built-in areas. Landsat 8 SR was biased over the VIS bands (-9 ~ -7.6%). BRDF normalization just contributed to a minor improvement. Our results demonstrate the potential of drone HSI to replace in-situ observation and evaluate SR or atmospheric correction algorithms over the flat terrain. Future researches should replicate the results over the complex terrain and canopy structure (i.e. forest).์›๊ฒฉํƒ์‚ฌ์—์„œ ์ง€ํ‘œ ๋ฐ˜์‚ฌ๋„(SR)๋Š” ์ง€ํ‘œ์ •๋ณด๋ฅผ ๋น„ํŒŒ๊ดด์ ์ด๊ณ  ์ฆ‰๊ฐ์ ์ธ ๋ฐฉ๋ฒ•์œผ๋กœ ์ „๋‹ฌํ•ด์ฃผ๋Š” ๋งค๊ฐœ์ฒด ์—ญํ• ์„ ํ•œ๋‹ค. ์‹ ๋ขฐํ•  ์ˆ˜ ์žˆ๋Š” SR์€ ์œก์ƒ ์ƒํƒœ๊ณ„ ๋ชจ๋ธ๋ง์˜ ๊ธฐ๋ณธ์ด๊ณ , ์ด์— ๋”ฐ๋ผ SR์˜ ์‹œ๊ณต๊ฐ„์  ๊ฒ€์ฆ์ด ์š”๊ตฌ๋œ๋‹ค. ์ผ๋ฐ˜์ ์œผ๋กœ SR์€ ์—ฌ๋Ÿฌ ์ง€์ƒ ๊ธฐ์ค€์ (GCP)์„ ๊ธฐ๋ฐ˜์œผ๋กœ ํ•˜๋Š” ํ˜„์žฅ ๋ถ„๊ด‘๋ฒ•์„ ํ†ตํ•ด์„œ ์‹œ๊ฐ„์  ์—ฐ์†์„ฑ์ด ๋ณด์žฅ๋œ๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ํ˜„์žฅ ๋ถ„๊ด‘๋ฒ•์€ ์ œํ•œ์ ์ธ ์ƒ˜ํ”Œ๋ง์œผ๋กœ ๊ณต๊ฐ„ ํŒจํ„ด์„ ๊ฑฐ์˜ ๋ณด์—ฌ์ฃผ์ง€ ์•Š์•„, ์œ„์„ฑ SR์˜ ํ”ฝ์…€ ๋ณ„ ๊ณต๊ฐ„ ๋ณ€๋™์„ฑ์€ ์ž˜ ๋ถ„์„๋˜์ง€ ์•Š์•˜๋‹ค. ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ๋“œ๋ก  ๊ธฐ๋ฐ˜์˜ ์ดˆ๋ถ„๊ด‘ ์˜์ƒ(HSI)์„ ์ฐธ๊ณ ์ž๋ฃŒ๋กœ ๋„์ž…ํ•˜์—ฌ, ์ด๋ฅผ ์ด์งˆ์ ์ธ ๋…ผ ๊ฒฝ๊ด€์—์„œ Sentinel 2 ๋ฐ Landsat 8 SR๊ณผ ๋น„๊ตํ•˜์˜€๋‹ค. ์šฐ์„ , ๋“œ๋ก  HSI๋Š” ํ˜„์žฅ ๋ถ„๊ด‘๋ฒ• ๋ฐ ๊ฒฝ๋กœ ์ค‘์ฒฉ์„ ํ†ตํ•ด์„œ ๊ด€์ธก๊ฐ๋„ ๋ฒ”์œ„ ๋‚ด์—์„œ ์ •์„ฑ์ ์ธ ๋ฐฉ์‚ฌ ์ธก์ •์„ ๋ณด์žฅํ•œ๋‹ค๊ณ  ๊ฒ€์ฆ๋˜์—ˆ๋‹ค. ์ดํ›„, ๋“œ๋ก  HSI๋Š” ์œ„์„ฑ SR์˜ ๋ถ„๊ด‘๋ฐ˜์‘ํŠน์„ฑ, ๊ณต๊ฐ„ํ•ด์ƒ๋„ ๋ฐ ์ขŒํ‘œ๊ณ„๋ฅผ ๊ธฐ์ค€์œผ๋กœ ๋งž์ถฐ์กŒ๊ณ , ๊ด€์ธก ๊ธฐํ•˜๋ฅผ ํ†ต์ผํ•˜๊ธฐ ์œ„ํ•ด์„œ ๋“œ๋ก  HIS์™€ ์œ„์„ฑ SR์€ ๊ฐ๊ฐ ์–‘๋ฐฉํ–ฅ๋ฐ˜์‚ฌ์œจ๋ถ„ํฌํ•จ์ˆ˜ (BRDF) ์ •๊ทœํ™” ๋ฐ˜์‚ฌ๋„ (NBAR)๋กœ ๋ณ€ํ™˜๋˜์—ˆ๋‹ค. ๋งˆ์ง€๋ง‰์œผ๋กœ, 1) APU ํ–‰๋ ฌ์œผ๋กœ ์œ„์„ฑ SR๊ณผ NDVI, NIRv๋ฅผ ํฌํ•จํ•˜๋Š” ์‹์ƒ์ง€์ˆ˜(VI)์˜ ๊ณต๊ฐ„๋ณ€๋™์„ฑ์„ ์ •๋Ÿ‰ํ™” ํ–ˆ๊ณ , 2) ๋Œ€๊ธฐ๋ณด์ •์˜ ์ด๋ก ์  ์˜ค์ฐจ๋ฅผ ๊ธฐ์ค€์œผ๋กœ SR๊ณผ VI๋ฅผ ํ”ฝ์…€๋ณ„๋กœ ํ‰๊ฐ€ํ–ˆ๊ณ , 3) BRDF ์ •๊ทœํ™”๋ฅผ ํ†ตํ•œ ๊ฐœ์„  ์‚ฌํ•ญ์„ ๊ฒ€ํ† ํ–ˆ๋‹ค. Sentinel 2 SR์€ ๋“œ๋ก  HSI์™€ ์ „๋ฐ˜์ ์œผ๋กœ ์ข‹์€ ์ผ์น˜๋ฅผ ๋ณด์ด๋‚˜, ๋‘ NIR ์ฑ„๋„์€ ์ตœ๋Œ€ 10% ํŽธํ–ฅ๋˜์—ˆ๋‹ค. NIR์˜ ํŽธํ–ฅ์€ ์‹์ƒ์ง€์ˆ˜์—์„œ ํ† ์ง€ ํ”ผ๋ณต์— ๋”ฐ๋ผ ๋‹ค๋ฅธ ์˜ํ–ฅ์„ ๋ฏธ์ณค๋‹ค. NDVI๋Š” ์‹์ƒ์—์„œ๋Š” ๋‚ฎ์€ ํŽธํ–ฅ์„ ๋ณด์—ฌ์คฌ๊ณ , NIRv๋Š” ๋„์‹œ์‹œ์„ค๋ฌผ ์˜์—ญ์—์„œ๋งŒ ๋†’์€ ํŽธํ–ฅ์„ ๋ณด์˜€๋‹ค. Landsat 8 SR์€ VIS ์ฑ„๋„์— ๋Œ€ํ•ด ํŽธํ–ฅ๋˜์—ˆ๋‹ค (-9 ~ -7.6%). BRDF ์ •๊ทœํ™”๋Š” ์œ„์„ฑ SR์˜ ํ’ˆ์งˆ์„ ๊ฐœ์„ ํ–ˆ์ง€๋งŒ, ๊ทธ ์˜ํ–ฅ์€ ๋ถ€์ˆ˜์ ์ด์—ˆ๋‹ค. ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ํ‰ํƒ„ํ•œ ์ง€ํ˜•์—์„œ ๋“œ๋ก  HSI๊ฐ€ ํ˜„์žฅ ๊ด€์ธก์„ ๋Œ€์ฒดํ•  ์ˆ˜ ์žˆ๊ณ , ๋”ฐ๋ผ์„œ ์œ„์„ฑ SR์ด๋‚˜ ๋Œ€๊ธฐ๋ณด์ • ์•Œ๊ณ ๋ฆฌ์ฆ˜์„ ํ‰๊ฐ€ํ•˜๋Š”๋ฐ ํ™œ์šฉ๋  ์ˆ˜ ์žˆ๋‹ค๋Š” ๊ฒƒ์„ ๋ณด์˜€๋‹ค. ํ–ฅํ›„ ์—ฐ๊ตฌ์—์„œ๋Š” ์‚ฐ๋ฆผ์œผ๋กœ ๋Œ€์ƒ์ง€๋ฅผ ํ™•๋Œ€ํ•˜์—ฌ, ์ง€ํ˜•๊ณผ ์บ๋…ธํ”ผ ๊ตฌ์กฐ๊ฐ€ ๋“œ๋ก  HSI ๋ฐ ์œ„์„ฑ SR์— ๋ฏธ์น˜๋Š” ์˜ํ–ฅ์„ ๋ถ„์„ํ•  ํ•„์š”๊ฐ€ ์žˆ๋‹ค.Chapter 1. Introduction 1 1.1 Background 1 Chapter 2. Method 3 2.1 Study Site 3 2.2 Drone campaign 4 2.3 Data processing 4 2.3.1 Sensor calibration 5 2.3.2 Bidirectional reflectance factor (BRF) calculation 7 2.3.3 BRDF correction 7 2.3.4 Orthorectification 8 2.3.5 Spatial Aggregation 9 2.3.6 Co-registration 10 2.4 Satellite dataset 10 2.4.2 Landsat 8 12 Chapter 3. Result and Discussion 12 3.1 Drone BRF map quality assessment 12 3.1.1 Radiometric accuracy 12 3.1.2 BRDF effect 15 3.2 Spatial variability in satellite surface reflectance product 16 3.2.1 Sentinel 2B (10m) 17 3.2.2 Sentinel 2B (20m) 22 3.2.3 Landsat 8 26 Chapter 4. Conclusion 28 Supplemental Materials 30 Bibliography 34 Abstract in Korean 43์„

    Remote Sensing of Environment: Current status of Landsat program, science, and applications

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    Formal planning and development of what became the first Landsat satellite commenced over 50 years ago in 1967. Now, having collected earth observation data for well over four decades since the 1972 launch of Landsat- 1, the Landsat program is increasingly complex and vibrant. Critical programmatic elements are ensuring the continuity of high quality measurements for scientific and operational investigations, including ground systems, acquisition planning, data archiving and management, and provision of analysis ready data products. Free and open access to archival and new imagery has resulted in a myriad of innovative applications and novel scientific insights. The planning of future compatible satellites in the Landsat series, which maintain continuity while incorporating technological advancements, has resulted in an increased operational use of Landsat data. Governments and international agencies, among others, can now build an expectation of Landsat data into a given operational data stream. International programs and conventions (e.g., deforestation monitoring, climate change mitigation) are empowered by access to systematically collected and calibrated data with expected future continuity further contributing to the existing multi-decadal record. The increased breadth and depth of Landsat science and applications have accelerated following the launch of Landsat-8, with significant improvements in data quality. Herein, we describe the programmatic developments and institutional context for the Landsat program and the unique ability of Landsat to meet the needs of national and international programs. We then present the key trends in Landsat science that underpin many of the recent scientific and application developments and followup with more detailed thematically organized summaries. The historical context offered by archival imagery combined with new imagery allows for the development of time series algorithms that can produce information on trends and dynamics. Landsat-8 has figured prominently in these recent developments, as has the improved understanding and calibration of historical data. Following the communication of the state of Landsat science, an outlook for future launches and envisioned programmatic developments are presented. Increased linkages between satellite programs are also made possible through an expectation of future mission continuity, such as developing a virtual constellation with Sentinel-2. Successful science and applications developments create a positive feedback loopโ€”justifying and encouraging current and future programmatic support for Landsat
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