127 research outputs found

    Assessment of Normalized Water-Leaving Radiance Derived From Goci Using AERONET-OC Data

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    The geostationary ocean color imager (GOCI), as the worldโ€™s first operational geostationary ocean color sensor, is aiming at monitoring short-term and small-scale changes of waters over the northwestern Pacific Ocean. Before assessing its capability of detecting subdiurnal changes of seawater properties, a fundamental understanding of the uncertainties of normalized water-leaving radiance (nLw) products introduced by atmospheric correction algorithms is necessarily required. This paper presents the uncertainties by accessing GOCI-derived nLw products generated by two commonly used operational atmospheric algorithms, the Korea Ocean Satellite Center (KOSC) standard atmospheric algorithm adopted in GOCI Data Processing System (GDPS) and the NASA standard atmospheric algorithm implemented in Sea-Viewing Wide Field-of-View Sensor Data Analysis System (SeaDAS/l2gen package), with Aerosol Robotic Network Ocean Color (AERONET-OC) provided nLw data. The nLw data acquired from the GOCI sensor based on two algorithms and four AERONET-OC sites of Ariake, Ieodo, Socheongcho, and Gageocho from October 2011 to March 2019 were obtained, matched, and analyzed. The GDPS-generated nLw data are slightly better than that with SeaDAS at visible bands; however, the mean percentage relative errors for both algorithms at blue bands are over 30%. The nLw data derived by GDPS is of better quality both in clear and turbid water, although underestimation is observed at near-infrared (NIR) band (865 nm) in turbid water. The nLw data derived by SeaDAS are underestimated in both clear and turbid water, and the underestimation worsens toward short visible bands. Moreover, both algorithms perform better at noon (02 and 03 Universal Time Coordinated (UTC)), and worse in the early morning and late afternoon. It is speculated that the uncertainties in nLw measurements arose from aerosol models, NIR water-leaving radiance correction method, and bidirectional reflectance distribution function (BRDF) correction method in corresponding atmospheric correction procedure

    Dual Branch Neural Network for Sea Fog Detection in Geostationary Ocean Color Imager

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    Sea fog significantly threatens the safety of maritime activities. This paper develops a sea fog dataset (SFDD) and a dual branch sea fog detection network (DB-SFNet). We investigate all the observed sea fog events in the Yellow Sea and the Bohai Sea (118.1{\deg}E-128.1{\deg}E, 29.5{\deg}N-43.8{\deg}N) from 2010 to 2020, and collect the sea fog images for each event from the Geostationary Ocean Color Imager (GOCI) to comprise the dataset SFDD. The location of the sea fog in each image in SFDD is accurately marked. The proposed dataset is characterized by a long-time span, large number of samples, and accurate labeling, that can substantially improve the robustness of various sea fog detection models. Furthermore, this paper proposes a dual branch sea fog detection network to achieve accurate and holistic sea fog detection. The poporsed DB-SFNet is composed of a knowledge extraction module and a dual branch optional encoding decoding module. The two modules jointly extracts discriminative features from both visual and statistical domain. Experiments show promising sea fog detection results with an F1-score of 0.77 and a critical success index of 0.63. Compared with existing advanced deep learning networks, DB-SFNet is superior in detection performance and stability, particularly in the mixed cloud and fog areas

    ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ์˜ ๋Œ€๊ธฐ๋ณด์ • ๋ฐ ๋Œ€๋ฆฌ๊ต์ • ์—ฐ๊ตฌ

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    ๋ณธ ํ•™์œ„๋…ผ๋ฌธ์€ ์„ธ๊ณ„์ตœ์ดˆ์˜ ์ •์ง€๊ถค๋„ ํ•ด์ƒ‰ ์œ„์„ฑ์ธ ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘ ์œ„์„ฑ (GOCI : Geostationary Ocean Color Imager)์— ํ‘œ์ค€์œผ๋กœ ์‚ฌ์šฉ๋˜๋Š” ๋Œ€๊ธฐ๋ณด์ • ์ด๋ก ์— ๋Œ€ํ•˜์—ฌ ๊ธฐ์ˆ ํ•˜๊ณ  ์žˆ๋‹ค. ํƒ€ ๊ทน๊ถค๋„ ํ•ด์ƒ‰์œ„์„ฑ๋“ค์ด 1~2์ผ ์ฃผ๊ธฐ๋กœ ํ•œ ์žฅ์†Œ๋ฅผ ๋ฐฉ๋ฌธํ•˜๋ฉฐ ์ „ ์ง€๊ตฌ๋ฅผ ๊ด€์ธกํ•˜๋Š” ๊ฒƒ๊ณผ ๋‹ฌ๋ฆฌ ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ์€ ํ•œ๋ฐ˜๋„๋ฅผ ํฌํ•จํ•œ ๋™๋ถ์•„ํ•ด์—ญ์„ 0.5 km ๊ณต๊ฐ„ํ•ด์ƒ๋„๋กœ ๋‚ฎ ์‹œ๊ฐ„ ๋™์•ˆ 1์‹œ๊ฐ„์˜ ์‹œ๊ฐ„๊ฐ„๊ฒฉ์œผ๋กœ ๊ด€์ธกํ•˜๊ณ  ์žˆ์œผ๋ฉฐ (ํ•˜๋ฃจ 8ํšŒ ๊ด€์ธก) ๊ฐ€์‹œ๊ด‘~๊ทผ์ ์™ธํŒŒ์žฅ๋Œ€ (412, 443, 490, 555, 660, 680, 745, 865 nm) ์˜์—ญ์—์„œ ๊ด€์ธกํ•œ๋‹ค. ๋Œ€๊ธฐ์ƒ์ธต ์œ„์„ฑ๊ถค๋„์—์„œ ์ผ๋ฐ˜์ ์ธ ๋ง‘์€ ํ•ด์—ญ์„ ๋Œ€์ƒ์œผ๋กœ ๊ด€์ธก๋œ ๊ฐ€์‹œ๊ด‘~๊ทผ์ ์™ธํŒŒ์žฅ๋Œ€ ์‹ ํ˜ธ ์ค‘ 90%์ด์ƒ์€ ๋Œ€๊ธฐ์‹ ํ˜ธ์ด๋ฉฐ, ํ•ด์ˆ˜์‹ ํ˜ธ์˜ ํฌ๊ธฐ๋Š” 10% ๋ฏธ๋งŒ์„ ์ฐจ์ง€ํ•œ๋‹ค. ๋Œ€๊ธฐ์‹ ํ˜ธ์˜ ํฌ๊ธฐ๊ฐ€ ํ•ด์ˆ˜์‹ ํ˜ธ์˜ ํฌ๊ธฐ๋ณด๋‹ค 10๋ฐฐ ์ด์ƒ ํฌ๊ธฐ ๋•Œ๋ฌธ์— 1%์˜ ๋Œ€๊ธฐ์‹ ํ˜ธ ์ถ”์ • ์˜ค์ฐจ๋Š” 10%์ด์ƒ์˜ ํ•ด์ˆ˜ ๊ด‘ ์ŠคํŽ™ํŠธ๋Ÿผ ์ถ”์ •์˜ค๋ฅ˜๋ฅผ ์ผ์œผํ‚จ๋‹ค. ์ด๋Ÿฐ ์ด์œ ๋กœ ์œ„์„ฑ์„ ํ†ตํ•œ ํ•ด์ƒ‰์›๊ฒฉํƒ์‚ฌ ์ž„๋ฌด๋Š” ๋†’์€ ๋Œ€๊ธฐ๋ณด์ • ์ •๋ฐ€๋„๋ฅผ ์š”๊ตฌํ•˜๊ณ  ์žˆ์œผ๋ฉฐ ๋Œ€๊ธฐ๋ณด์ •์˜ ๊ฐœ๋ฐœ์ด ํ•ด์ƒ‰์›๊ฒฉํƒ์‚ฌ ์•Œ๊ณ ๋ฆฌ์ฆ˜ ๊ฐœ๋ฐœ ์ค‘ ๊ฐ€์žฅ ํ•ต์‹ฌ์ด ๋œ๋‹ค. ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ ํ‘œ์ค€ ๋Œ€๊ธฐ๋ณด์ •์€ NASA๊ฐ€ ํ•ด์ƒ‰์›๊ฒฉํƒ์‚ฌ ์ž„๋ฌด๋ฅผ ์œ„ํ•ด ๊ฐœ๋ฐœํ•œ SeaWiFS ํ‘œ์ค€ ๋Œ€๊ธฐ๋ณด์ •์— ์ด๋ก ์ ์ธ ๊ธฐ๋ฐ˜์„ ๋‘๊ณ  ์žˆ๋‹ค. SeaWiFS ๋ฐฉ๋ฒ•์€ ์šฐ์„  ๋‘๊ฐœ์˜ ๊ทผ์ ์™ธ ํŒŒ์žฅ๋Œ€ ๊ด€์ธก๊ฒฐ๊ณผ์™€ ๋ณต์‚ฌ์ „๋‹ฌ์‹œ๋ฎฌ๋ ˆ์ด์…˜ ๊ฒฐ๊ณผ(์กฐ๊ฒฌํ‘œ)๋ฅผ ์„œ๋กœ ๋น„๊ตํ•˜์—ฌ ๋Œ€๊ธฐ ์ค‘ ์—์–ด๋กœ์กธ ์ž…์ž์˜ ์ข…๋ฅ˜ ๋ฐ ๋†๋„ ์ตœ์ ๊ฐ’์„ ์ถ”์ •ํ•ด ๋‚ด๋ฉฐ ์ด ์ถ”์ •๊ฒฐ๊ณผ๋ฅผ ๋ฐ”ํƒ•์œผ๋กœ ๋ชจ๋“  ๊ฐ€์‹œ๊ด‘ ํŒŒ์žฅ์˜ ์—์–ด๋กœ์กธ ๋ฐ˜์‚ฌ๋„ ์ŠคํŽ™ํŠธ๋Ÿผ์„ ๋‹ค์‹œ ์กฐ๊ฒฌํ‘œ๋ฅผ ์ด์šฉํ•˜์—ฌ ๊ณ„์‚ฐํ•œ๋‹ค. ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ์˜ ๋Œ€๊ธฐ๋ณด์ •๋„ ์œ ์‚ฌํ•˜๊ฒŒ ๋‘ ๊ทผ์ ์™ธํŒŒ์žฅ๋Œ€ ์—์–ด๋กœ์กธ ๋ฐ˜์‚ฌ๋„ ์ƒ๊ด€๊ด€๊ณ„๋ฅผ ์ด์šฉํ•˜์—ฌ ์—์–ด๋กœ์กธ ์ข…๋ฅ˜ ๋ฐ ๋†๋„๋ฅผ ๊ณ„์‚ฐํ•˜๋Š”๋ฐ, ์ด ์—ฐ๊ตฌ๋ฅผ ํ†ตํ•˜์—ฌ SeaWiFS ๋ฐ ๋‹ค๋ฅธ ์œ ์‚ฌ ๋Œ€๊ธฐ๋ณด์ • ๋ฐฉ๋ฒ•๋“ค๊ณผ ๋น„๊ตํ•˜์—ฌ ์ •ํ™•๋„ ๋ฟ ์•„๋‹ˆ๋ผ ๊ณ„์‚ฐ ํšจ์œจ ๋˜ํ•œ ๊ฐœ์„ ํ•˜์˜€๋‹ค. ์ถ”๊ฐ€์ ์œผ๋กœ SeaWiFS์— ์ ์šฉ๋œ ์ˆ˜์ฆ๊ธฐ ํก๊ด‘ ๋ณด์ • ๋ชจ๋ธ์„ ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ์˜ ๋ถ„๊ด‘ํŠน์„ฑ์— ๋งž๊ฒŒ ์ˆ˜์ •ํ•˜์—ฌ ์ ์šฉํ•˜์˜€์œผ๋ฉฐ, ํƒ๋„๊ฐ€ ๋†’์€ ํ•ด์—ญ์—์„œ ๋Œ€๊ธฐ๋ณด์ • ์˜ค์ฐจ๋ฅผ ์ค„์ด๋Š” ๋ฐฉ๋ฒ•๋„ ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ ๊ด€์ธก์˜์—ญ์˜ ํ•ด์ˆ˜ ๊ด‘ ํŠน์„ฑ ๋ฐ ๋ฐ˜์‚ฌ๋„ ์ •๋ณด๋“ค์„ ์ด์šฉํ•˜์—ฌ ๊ฐœ๋ฐœํ•˜์˜€๋‹ค. ์ดˆ๊ธฐ๋ฒ„์ „์˜ ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ ํ‘œ์ค€ ๋Œ€๊ธฐ๋ณด์ •์˜ ๊ฒ€๋ณด์ • ๊ฒฐ๊ณผ ํƒ๋„๊ฐ€ ๋†’์€ ์—ฐ์•ˆํ•ด์—ญ์—์„œ๋Š” 10% ๋‚ด์™ธ์˜ ๋งŒ์กฑํ•  ๋งŒํ•œ ์˜ค์ฐจ์ˆ˜์ค€์„ ๋ณด์—ฌ์ฃผ์—ˆ์œผ๋‚˜, ํƒ๋„๊ฐ€ ๋‚ฎ์€ ํ•ด์—ญ์—์„œ๋Š” 50% ์ด์ƒ์˜ ์˜ค์ฐจ๋ฅผ ๋ฐœ์ƒ๋˜์—ˆ๋‹ค. ์ด๋Š” ๋Œ€๋ฆฌ๊ต์ • ์ˆ˜ํ–‰์˜ ๋ถ€์žฌ๊ฐ€ ์ฃผ๋œ ์š”์ธ์ด๋ฉฐ, ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ์ด๋ฅผ ๋ณด์™„ํ•˜๊ธฐ ์œ„ํ•ด SeaWiFS ํ‘œ์ค€ ๋Œ€๋ฆฌ๊ต์ • ํ”„๋กœ์„ธ์Šค์— ๊ธฐ๋ฐ˜์„ ๋‘๊ณ  ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ์— ๋งž๊ฒŒ ๋Œ€๋ฆฌ๊ต์ •์„ ์ˆ˜ํ–‰ํ•˜์˜€๋‹ค. ์ด ๋Œ€๋ฆฌ๊ต์ • ๋ฐฉ๋ฒ•์—์„œ๋Š” ํŠน์ • ํ•ด์—ญ์˜ ์—์–ด๋กœ์กธ ๊ด‘ํŠน์„ฑ์ด ํ•ญ์ƒ ํ•ด์–‘์„ฑ ์—์–ด๋กœ์กธ์ด๋ผ ๊ฐ€์ •ํ•˜๊ณ  ์ด๋ฅผ ๋ฐ”ํƒ•์œผ๋กœ ๊ทผ์ ์™ธ ํŒŒ์žฅ๋Œ€ ์œ„์„ฑ ๊ด€์ธก ์กฐ๋„๋ฅผ ์‹œ๋ฎฌ๋ ˆ์ด์…˜ ํ•˜์—ฌ ๋‘ ๊ทผ์ ์™ธ ํŒŒ์žฅ๋Œ€๋ฅผ ๋จผ์ € ์ƒ๋Œ€๊ต์ • ํ•œ๋‹ค. ์ดํ›„, ์ƒ๋Œ€๊ต์ •๋œ ๋‘ ๊ทผ์ ์™ธ ํŒŒ์žฅ๋Œ€๋ฅผ ์ด์šฉํ•˜๋ฉด ๋ง‘์€ ํ•ด์—ญ์—์„œ ๋ณต์‚ฌ์ „๋‹ฌ์‹œ๋ฎฌ๋ ˆ์ด์…˜์„ ํ†ตํ•˜์—ฌ ๊ฐ€์‹œ๊ด‘ ํŒŒ์žฅ๋Œ€ ๋Œ€๊ธฐ์กฐ๋„๋ฅผ ๋ชจ์˜ ํ•  ์ˆ˜ ์žˆ๊ฒŒ ๋˜๊ณ , ์—ฌ๊ธฐ์— ๋ง‘์€ ํ•ด์—ญ์˜ ํ˜„์žฅ ๊ด‘ ์ธก์ • ์ž๋ฃŒ๊ฐ€ ์ถ”๊ฐ€๋˜๋ฉด ๊ฐ€์‹œ๊ด‘ํŒŒ์žฅ๋Œ€ ์œ„์„ฑ๊ด€์ธก์กฐ๋„์˜ ์‹œ๋ฎฌ๋ ˆ์ด์…˜์ด ๊ฐ€๋Šฅํ•˜๋‹ค. ์ด ๊ฐ€์‹œ๊ด‘ํŒŒ์žฅ๋Œ€ ๋ชจ์˜ ๊ฒฐ๊ณผ์™€ ์‹ค์ œ ์œ„์„ฑ๊ด€์ธก์กฐ๋„์™€ ๋น„๊ตํ•˜๋ฉด ๊ฐ€์‹œ๊ด‘ํŒŒ์žฅ๋Œ€ ๋Œ€๋ฆฌ๊ต์ •์„ ์™„๋ฃŒํ•  ์ˆ˜ ์žˆ๋‹ค. ๋ณธ ๋Œ€๋ฆฌ๊ต์ • ๊ฒฐ๊ณผ ๋Œ€๋ฆฌ๊ต์ • ์ƒ์ˆ˜๊ฐ€ ์ตœ๋Œ€ 3.2% ๋ฐ”๋€Œ์—ˆ์œผ๋ฉฐ (490 nm ๋ฐด๋“œ) ์ƒˆ ๋Œ€๋ฆฌ๊ต์ • ์ƒ์ˆ˜ ์ ์šฉ ์‹œ ๋ง‘์€ ํ•ด์—ญ ๋Œ€๊ธฐ๋ณด์ • ์ •ํ™•๋„๊ฐ€ ์ตœ๋Œ€ 50% ์ด์ƒ ์ƒ์Šนํ•˜์˜€๋‹ค. ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ์ฒœ๋ฆฌ์•ˆํ•ด์–‘์œ„์„ฑ ๋Œ€๊ธฐ๋ณด์ •์˜ ์„ฑ๋Šฅ์„ ํ‰๊ฐ€ํ•˜๊ธฐ ์œ„ํ•ด์„œ ๋Œ€๊ธฐ๋ณด์ • ๊ฒฐ๊ณผ ์›๊ฒฉ๋ฐ˜์‚ฌ๋„ (remote-sensing reflectance: Rrs)๋ฅผ ํ•œ๊ตญํ•ด์–‘๊ณผํ•™๊ธฐ์ˆ ์› ํ•ด์–‘์œ„์„ฑ์—ฐ๊ตฌ์„ผํ„ฐ์—์„œ 2010๋…„ ์ดํ›„๋กœ ํ•œ๋ฐ˜๋„ ์ฃผ๋ณ€ ํ•ด์—ญ ํ˜„์žฅ์กฐ์‚ฌ๋ฅผ ํ†ตํ•ด ์ˆ˜์ง‘ํ•œ ์›๊ฒฉ๋ฐ˜์‚ฌ๋„ ์ž๋ฃŒ๋“ค๊ณผ ๋น„๊ต๊ฒ€์ • ํ•˜์˜€์œผ๋ฉฐ, ๊ฒ€์ •๊ฒฐ๊ณผ 76, 84, 88, 90, 81, 82%์˜ ์ •ํ™•๋„๋ฅผ ๋ณด์—ฌ์ฃผ์—ˆ๋‹ค. ์ถ”๊ฐ€๋กœ ํ˜„์žฅ์ž๋ฃŒ๊ฐ€ ์•„๋‹Œ ์‹œ๋ฎฌ๋ ˆ์ด์…˜ ์ž๋ฃŒ๋ฅผ ํ†ตํ•ด ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ ์•Œ๊ณ ๋ฆฌ์ฆ˜ ๋ฟ ์•„๋‹ˆ๋ผ ๋‹ค๋ฅธ ํ•ด์ƒ‰์›๊ฒฉํƒ์‚ฌ ์ž„๋ฌด๋ฅผ ์œ„ํ•ด ๊ฐœ๋ฐœ๋œ ์ฃผ์š” ๋Œ€๊ธฐ๋ณด์ • ์•Œ๊ณ ๋ฆฌ์ฆ˜๋“ค ๊ตฌํ˜„ํ•˜์—ฌ ํ•จ๊ป˜ ๋น„๊ต๊ฒ€์ฆ ํ•˜์˜€๊ณ , ๋ณธ ๋น„๊ต๊ฒ€์ฆ์—์„œ๋„ ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ ํ‘œ์ค€ ๋Œ€๊ธฐ๋ณด์ •์ด ๋‹ค๋ฅธ ๋Œ€๊ธฐ๋ณด์ • ๋ฐฉ๋ฒ•๋“ค๊ณผ ๋น„๊ตํ•˜์—ฌ ๊ฐ€์žฅ ๋‚ฎ์€ ์˜ค์ฐจ์œจ์„ ๋ณด์—ฌ์ฃผ์—ˆ์œผ๋ฉฐ, ํŠนํžˆ ๋‹ค์ค‘์‚ฐ๋ž€ ํšจ๊ณผ๊ฐ€ ํฐ ์ž‘์€ ์ž…์žํฌ๊ธฐ์˜ ์—์–ด๋กœ์กธ ๋ชจ๋ธ์—์„œ ๋” ์ข‹์€ ์„ฑ๋Šฅ์„ ๋ณด์—ฌ์ฃผ์—ˆ๋‹ค. ๋ณธ ์—ฐ๊ตฌ๊ฒฐ๊ณผ๋Š” ์ด๋ก ์ ์œผ๋กœ SeaWiFS ๋“ฑ ๋น„์Šทํ•œ ๋ฐด๋“œ ํŠน์„ฑ์„ ๊ฐ€์ง„ ํƒ€ ํ•ด์ƒ‰์œ„์„ฑ์˜ ๋Œ€๊ธฐ๋ณด์ •๋ฐฉ๋ฒ•์œผ๋กœ๋„ ์ ์šฉ์ด ๊ฐ€๋Šฅํ•˜๋ฉฐ, ์ฒœ๋ฆฌ์•ˆ ํ•ด์–‘์œ„์„ฑ ์ž๋ฃŒ์ฒ˜๋ฆฌ์‹œ์Šคํ…œ (GOCI data processing system: GDPS) 1.5๋ฒ„์ „์—์˜ ์ ์šฉ๋  ์˜ˆ์ •์ด๋‹ค.Chapter 1. Introduction 1 1.1 Ocean color remote sensing 1 1.2 Geostationary Ocean Color Imager (GOCI) 2 1.3 Atmospheric correction and vicarious calibration 5 Chapter 2. Initial atmospheric correction for the GOCI data 10 2.1 Introduction 10 2.2 Method 11 2.2.1 Correction for gaseous absorption and whitecap radiance 13 2.2.2 Solar irradiance normalization 15 2.2.3 Correction for molecular (Rayleigh) scattering 17 2.2.4 Cloud mask 18 2.2.5 Correction for multiple scattering by aerosols 19 2.2.6 Correction for atmospheric transmittance 22 2.2.7 Correction for near-infrared water reflectance over turbid waters 22 2.3 Conclusion 24 Chapter 3. Algorithm updates and vicarious calibration for the GOCI atmospheric correction 25 3.1 Backgrounds 25 3.2 Updates to the initial GOCI atmospheric correction algorithm 26 3.2.1 Correction for gaseous absorption and whitecap radiance 26 3.2.2 Sun-glint correction 28 3.2.3 Considering gravity effect for Rayleigh scattering 29 3.2.4 Correction for multiple scattering by aerosols - SRAMS 30 3.2.5 Correction for bidirectional effects for water reflectance 35 3.2.6 Correction for near-infrared water reflectance over turbid waters 39 3.2.7 Atmospheric transmittance with considering anisotropic angular distribution of water reflectance 40 3.3 Vicarious calibration of GOCI near-infrared bands 41 3.3.1 Method 44 3.3.2 Inter-calibration of GOCI near-infrared bands 45 3.3.3 Vicarious calibration of GOCI visible bands 49 Chapter 4. Validation results 51 4.1 Data 51 4.1.1 Synthetic data derived by simulations 51 4.1.2 In situ radiometric data measured from shipboard 52 4.1.3 AERONET-OC radiometric data 56 4.2 Validation of SRAMS scheme with simulation data 58 4.3 Assessment of the atmospheric correction improvements with in situ radiometric data 59 Chapter 5. Discussions 61 5.1 Impacts of water vapor correction on ocean color products 61 5.2 Stability for high solar and satellite zenith angle for diurnal observation 62 5.3 Cloud masking on fast-moving clouds and quality analysis 63 5.4 Evaluation of the GOCI aerosol correction scheme compared with other approaches 64 5.4.1 Aerosol correction approach for OCTS 64 5.4.2 Aerosol correction approach for MERIS 67 5.4.3 Evaluation results 69 5.5 Pitfalls in estimation of aerosol reflectance using 2-NIR bands 71 5.6 Issues in the vicarious calibration of GOCI VIS and NIR bands 72 5.7 Uncertainties from bidirectional effect 75 Chapter 6. Conclusion 76 Appendix. Glossary of symbols 82 Acknowledgements 86 References 88Docto

    A semi-analytical model for estimating total suspended matter in highly turbid waters

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    Total suspended matter (TSM) is related to water quality. High TSM concentrations limit underwater light availability, thus affecting the primary productivity of aquatic ecosystems. Accurate estimation of TSM concentrations in various waters with remote sensing technology is particularly challenging, as the concentrations and optical properties vary greatly among different waters. In this research, a semi-analytical model was established for Hangzhou Bay and Lake Taihu for estimating TSM concentration. The model construction proceeded in two steps. 1) Two indices of the model were calculated by deriving absorption and backscattering coefficients of suspended matter (ap(λ) and bbp(λ)) from the reflectance signal using a semi-analytical method. 2) The two indices were then weighted to derive TSM. The performance of the proposed model was tested using in situ reflectance and Geostationary Ocean Color Imager (GOCI) data. The derived TSM based on in situ reflectance and GOCI images both corresponded well with the in situ TSM with low mean relative error (32%, 41%), root mean square error (20.1 mg/L, 43.1 mg/L), and normalized root mean square error (33%, 55%). The model was further used for the slightly turbid Xin’anjiang Reservoir to demonstrate its applicability to derive ap(λ) and bbp(λ) in other water types. The results indicated that the form Rrs −1(λ1) − Rrs −1(λ2) could minimize the effect of CDOM absorption in deriving ap(λ) from the total absorption. The model exploited the different relationships between TSM concentration and multiband reflectance, thus improving the performance and application range in deriving TSM

    Sensor capability and atmospheric correction in ocean colour remote sensing

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    ยฉ 2015 by the authors; licensee MDPI, Basel, Switzerland. Accurate correction of the corrupting effects of the atmosphere and the water's surface are essential in order to obtain the optical, biological and biogeochemical properties of the water from satellite-based multi-and hyper-spectral sensors. The major challenges now for atmospheric correction are the conditions of turbid coastal and inland waters and areas in which there are strongly-absorbing aerosols. Here, we outline how these issues can be addressed, with a focus on the potential of new sensor technologies and the opportunities for the development of novel algorithms and aerosol models. We review hardware developments, which will provide qualitative and quantitative increases in spectral, spatial, radiometric and temporal data of the Earth, as well as measurements from other sources, such as the Aerosol Robotic Network for Ocean Color (AERONET-OC) stations, bio-optical sensors on Argo (Bio-Argo) floats and polarimeters. We provide an overview of the state of the art in atmospheric correction algorithms, highlight recent advances and discuss the possible potential for hyperspectral data to address the current challenges

    Uncertainties in the Geostationary Ocean Color Imager (GOCI) Remote Sensing Reflectance for Assessing Diurnal Variability of Biogeochemical Processes

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    Short-term (sub-diurnal) biological and biogeochemical processes cannot be fully captured by the current suite of polar-orbiting satellite ocean color sensors, as their temporal resolution is limited to potentially one clear image per day. Geostationary sensors, such as the Geostationary Ocean Color Imager (GOCI) from the Republic of Korea, allow the study of these short-term processes because their orbit permit the collection of multiple images throughout each day for any area within the sensors field of regard. Assessing the capability to detect sub-diurnal changes in in-water properties caused by physical and biogeochemical processes characteristic of open ocean and coastal ocean ecosystems, however, requires an understanding of the uncertainties introduced by the instrument and/or geophysical retrieval algorithms. This work presents a study of the uncertainties during the daytime period for an ocean region with characteristically low-productivity with the assumption that only small and undetectable changes occur in the in-water properties due to biogeochemical processes during the daytime period. The complete GOCI mission data were processed using NASAs SeaDAS/l2gen package. The assumption of homogeneity of the study region was tested using three-day sequences and diurnal statistics. This assumption was found to hold based on the minimal diurnal and day-to-day variability in GOCI data products. Relative differences with respect to the midday value were calculated for each hourly observation of the day in order to investigate what time of the day the variability is greater. Also, the influence of the solar zenith angle in the retrieval of remote sensing reflectances and derived products was examined. Finally, we determined that the uncertainties in water-leaving remote-sensing reflectance (Rrs) for the 412,443, 490, 555, 660 and 680 nm bands on GOCI are 8.05 x 10(exp -4), 5.49 x 10(exp -4), 4.48 x 10(exp -4), 2.51 x 10(exp -4), 8.83 x 10(exp -5), and 1.36 x 10(exp -4)/sr, respectively, and 1.09 x 10(exp -2)/cu.mgm for the chlorophyll-a concentration (Chl-a), 2.09 x 10(exp -3)/m for the absorption coefficient of chromophoric dissolved organic matter at 412 nm (a(sub g) (412)), and 3.7 mg/cu.m for particulate organic carbon (POC). These R(sub rs) values can be considered the threshold values for detectable changes of the in-water properties due to biological, physical or biogeochemical processes from GOCI

    Exploring Himawari-8 geostationary observations for the advanced coastal monitoring of the Great Barrier Reef

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    Larissa developed an algorithm to enable water-quality assessment within the Great Barrier Reef (GBR) using weather satellite observations collected every 10 minutes. This unprecedented temporal resolution records the dynamic nature of water quality fluctuations for the entire GBR, with applications for improved monitoring and management

    Reference solar irradiance spectra and consequences of their disparities in remote sensing of the ocean colour

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    International audienceSatellite ocean colour missions require a standard extraterrestrial solar irradiance spectrum in the visible and near-infrared (NIR) for use in the process of radiometric calibration, atmospheric correction and normalization of water-leaving radiances from in-situ measurements. There are numerous solar irradiance spectra (or models) currently in use within the ocean colour community and related domains. However, these irradiance spectra, constructed from single and/or multiple measurements sets or models, have noticeable differences ? ranging from about ยฑ1% in the NIR to ยฑ6% in the short wavelength region (ultraviolet and blue) ? caused primarily by the variation in the solar activity and uncertainties in experimental data from different instruments. Such differences between the applied solar irradiance spectra may have quite important consequences in reconciliation, comparison and validation of the products resulting from different ocean colour instruments. Thus, it is prudent to examine the model-to-model differences and ascertain an appropriate solar irradiance spectrum for use in future ocean colour research and validation purposes. This study first describes the processes which generally require the application of a solar irradiance spectrum, and then investigates the eight solar irradiance spectra (widely in use within the remote sensing community) selected on the basis of the following criteria: minimum spectral range of 350?1200 nm with adequate spectral resolution, completely or mostly based on direct measurements, minimal error range, intercomparison with other experiments and update of data. The differences in these spectra in absolute terms and in the SeaWiFS and MERIS in-band irradiances and their consequences on the retrieval algorithms of chlorophyll and suspended sediment are analyzed. Based on these detailed analyses, this study puts forward the solar irradiance spectrum most appropriate for all aspects of research, calibration and validation in ocean colour remote sensing. For an improved approximation of the extraterrestrial solar spectrum in the ultraviolet-NIR domain this study also proposes a new solar constant value determined from space-borne measurements of the last three decades

    Developments in Earth observation for the assessment and monitoring of inland, transitional, coastal and shelf-sea waters

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    The Earth's surface waters are a fundamental resource and encompass a broad range of ecosystems that are core to global biogeochemical cycling and food and energy production. Despite this, the Earth's surface waters are impacted by multiple natural and anthropogenic pressures and drivers of environmental change. The complex interaction between physical, chemical and biological processes in surface waters poses significant challenges for in situ monitoring and assessment and often limits our ability to adequately capture the dynamics of aquatic systems and our understanding of their status, functioning and response to pressures. Here we explore the opportunities that Earth observation (EO) has to offer to basin-scale monitoring of water quality over the surface water continuum comprising inland, transition and coastal water bodies, with a particular focus on the Danube and Black Sea region. This review summarises the technological advances in EO and the opportunities that the next generation satellites offer for water quality monitoring. We provide an overview of algorithms for the retrieval of water quality parameters and demonstrate how such models have been used for the assessment and monitoring of inland, transitional, coastal and shelf-sea systems. Further, we argue that very few studies have investigated the connectivity between these systems especially in large river-sea systems such as the Danube-Black Sea. Subsequently, we describe current capability in operational processing of archive and near real-time satellite data. We conclude that while the operational use of satellites for the assessment and monitoring of surface waters is still developing for inland and coastal waters and more work is required on the development and validation of remote sensing algorithms for these optically complex waters, the potential that these data streams offer for developing an improved, potentially paradigm-shifting understanding of physical and biogeochemical processes across large scale river-sea continuum including the Danube-Black Sea is considerable

    An empirical algorithm to seamlessly retrieve the concentration of suspended particulate matter from water color across ocean to turbid river mouths

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    Abstract(#br)We propose a globally applicable algorithm (GAA SPM ) to seamlessly retrieve the concentration of suspended particulate matter (SPM) ( C SPM ) from remote sensing reflectance ( R rs ( ฮป )) across ocean to turbid river mouths without any hard-switching in its application. GAA SPM is based on a calibrated relationship between C SPM and a generalized index for SPM ( GI SPM ) from water color. The GI SPM is mainly composed of three R rs ( ฮป ) ratios (671, 745, and 862 nm over 551 nm, respectively), along with weighting factors assigned to each ratio. The weighting factors are introduced to ensure the progressive application of R rs ( ฮป ) in the longer wavelengths for increasing C SPM . Calibration of GAA SPM employed data collected from multiple estuarine and coastal regions of Europe, China, Argentina, and the USA with the measured C SPM spanning from 0.2 to 2068.8 mg/L. Inter-comparison with several recalibrated well-known C SPM retrieval algorithms demonstrates that GAA SPM has the best retrieval accuracy over the entire C SPM range with a relative mean absolute difference (rMAD) of 41.3% (N = 437). This averaged uncertainty in GAA SPM -derived C SPM is mostly attributed to the retrievals from less turbid waters where C SPM < 50 mg/L (rMAD = 50%, N = 214). GAA SPM was further applied to the Visible Infrared Imaging Radiometer Suite (VIIRS) measurements over prominent coastal areas and produced reliable C SPM maps along with realistic spatial patterns. In contrast, applications of other C SPM algorithms resulted in less reliable C SPM maps with either unjustified numerical discontinuities in the C SPM spatial distribution or unsatisfactory retrieval accuracy. Therefore, we propose GAA SPM as a preferred algorithm to retrieve C SPM over regions with a wide range of C SPM , such as river plume areas
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