• 제목/요약/키워드: Stability transfer

검색결과 962건 처리시간 0.022초

GK-2A/AMI와 융합을 통한 GOCI-II 해색 산출물 정확도 개선 가능성 (GOCI-II Capability of Improving the Accuracy of Ocean Color Products through Fusion with GK-2A/AMI)

  • 이경상;안재현;박명숙
    • 대한원격탐사학회지
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    • 제37권5_2호
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    • pp.1295-1305
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    • 2021
  • 연안 및 대양의 효과적인 모니터링을 위해 여러 연구 분야에서 고품질의 위성 기반 해색 산출물들이 요구 있으며 이를 위해서는 정확한 대기 효과의 보정이 필수적이다. 현재 Geostationary Ocean ColorImage (GOCI)-II 지상시스템에서는 수증기 및 오존 등에 의한 가스 흡광 보정을 수행하기 위해 European Centre for Medium-Range Weather Forecasts (ECMWF) 또는 National Centers for Environmental Prediction (NCEP) 기상장 자료를 사용하고 있다. 이 과정에서 기상장 자료의 낮은 시공간해상도로 인해 오차가 발생할 수 있다. 따라서 본 연구에서는 복사 전달 모델 모의를 통해 개발된 GOCI-II의 수증기 흡광 보정 모델 및 GeoKompsat (GK)-2A/Advanced Meteorological Imager (AMI)의 가강수량 자료를 이용하여 수증기 흡광 효과를 보정하고 이에 따른 영향력을 분석하였다. 개발된 수증기 흡광 보정 모델 적용 유무에 따른 오차는 수증기의 영향이 적은 620 nm와 680 nm의 대기 상한 반사도에서 최대 1.3%와 0.27%로 적은 오차를 보였다. 그러나 수증기 흡광의 경향이 큰 709 nm 채널의 경우 태양 천정각 및 가강수량에 따라 6~15%의 큰 오차를 나타냈다. 레일리 보정 반사도에서는 대기 상한 반사도에서 발생한 오차가 크게 증폭되어 태양 천정각에 따라 GOCI-II의 각 밴드(620~865 nm) 별로 1.46~4.98, 7.53~19.53, 0.25~0.64, 14.74~40.5, 8.2~18.56, 5.7~11.9%의 큰 오차를 보이고 있다. 이는 수증기 흡광 보정이 해색 산출물의 정확도와 안정성에 큰 영향을 미칠 수 있다는 것을 의미하며, 향후 시공간 해상도가 높은 GK-2A/AMI와의 융합을 통해 GOCI-II 해색 산출물의 정확도 향상이 가능함을 시사한다.

Effect of micro-environment in ridge and southern slope on soil respiration in Quercus mongolica forest

  • Lee, Jae-Seok
    • Journal of Ecology and Environment
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    • 제42권4호
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    • pp.210-218
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    • 2018
  • Background: Soil respiration (Rs) is a major factor of the absorption and accumulation of carbon through photosynthesis in the ecosystem carbon cycle. This directly affects the amount of net ecosystem productivity, which affects the stability and sustainability of the ecosystem. Understanding the characteristics of Rs is indispensable to scientifically understand the carbon cycle of ecosystems. It is very important to study Rs characteristics through analysis of environmental factors closely related to Rs. Rs is affected by various environmental factors, such as temperature, precipitation, soil moisture, litter supply, organic matter content, dominant plant species, and soil disturbance. This study was conducted to analyze the effects of micro-topographical differences on Rs in forest vegetation by measuring the Rs on the ridge and southern slope sites of the broadly established Quercus mongolica forest in the central Korean area. Method: Rs, Ts, and soil moisture data were collected at the southern slope and ridge of the Q. mongolica forest in the Mt. Jeombong area in order to investigate the effects of topographical differences on Rs. Rs was collected by the closed chamber method, and data collection was performed from May 2011 to October 2013, except Winter seasons from November to April or May. For collecting the raw data of Rs in the field, acrylic collars were placed at the ridge and southern slope of the forest. The accumulated surface litter and the soil organic matter content (SOMC) were measured to a 5 cm depth. Based on these data, the Rs characteristics of the slope and ridge were analyzed. Results: Rs showed a distinct seasonal variation pattern in both the ridge and southern slope sites. In addition, Rs showed a distinct seasonal variation with high and low Ts changes. The average Rs measurements for the two sites, except for the Winter periods that were not measured, were $550.1\;mg\;CO_2m^{-2}h^{-1}$ at the ridge site and $289.4\;mg\;CO_2m^{-2}h^{-1}$ at the southern slope, a difference of 52.6%. There was no significant difference in the Rs difference between slopes except for the first half of 2013, and both sites showed a tendency to increase exponentially as Ts increased. In addition, although the correlation is low, the difference in Rs between sites tended to increase as Ts increased. SMC showed a large fluctuation at the southern slope site relative to the ridge site, as while it was very low in 2013, it was high in 2011 and 2012. The accumulated litter of the soil surface and the SOMC at the depth range of 0~5 cm were $874g\;m^{-2}$ and 23.3% at the ridge site, and $396g\;m^{-2}$ and 19.9% at the southern slope site. Conclusions: In this study, Rs was measured for the ridge and southern slope sites, which have two different results where the surface litter layer is disturbed by strong winds. The southern slope site shows that the litter layer formed in autumn due to strong winds almost disappeared, and while in the ridge site, it became thick due to the transfer of litter from the southern slope site. The mean Rs was about two times higher in the ridge site compared to that in the southern slope site. The Rs difference seems to be due to the difference in the amount of litter accumulated on the soil surface. As a result, the litter layer supplied to the soil surface is disturbed due to the micro-topographical difference, as the slope and the change of the community structure due to the plant season cause heterogeneity of the litter layer development, which in turn affects SMC and Rs. Therefore, it is necessary to introduce and understand these micro-topographical features and mechanisms when quantifying and analyzing the Rs of an ecosystem.