222 research outputs found

    Assessment of climate variability of the Greenland Ice Sheet: Integration of in situ and satellite data

    Get PDF
    The proposed research involves the application of multispectral satellite data in combination with ground truth measurements to monitor surface properties of the Greenland Ice Sheet which are essential for describing the energy and mass of the ice sheet. Several key components of the energy balance are parameterized using satellite data and in situ measurements. The analysis will be done for a ten year time period in order to get statistics on the seasonal and interannual variations of the surface processes and the climatology. Our goal is to investigate to what accuracy and over what geographic areas large scale snow properties and radiative fluxes can be derived based upon a combination of available remote sensing and meteorological data sets. Operational satellite sensors are calibrated based on ground measurements and atmospheric modeling prior to large scale analysis to ensure the quality of the satellite data. Further, several satellite sensors of different spatial and spectral resolution are intercompared to access the parameter accuracy. Proposed parameterization schemes to derive key component of the energy balance from satellite data are validated. For the understanding of the surface processes a field program was designed to collect information on spectral albedo, specular reflectance, soot content, grain size and the physical properties of different snow types. Further, the radiative and turbulent fluxes at the ice/snow surface are monitored for the parameterization and interpretation of the satellite data. The expected results include several baseline data sets of albedo, surface temperature, radiative fluxes, and different snow types of the entire Greenland Ice Sheet. These climatological data sets will be of potential use for climate sensitivity studies in the context of future climate change

    Tree Cover Variability in the District of Columbia

    Get PDF
    Urban forests are increasingly a focus of interest as urbanized populations grow and urban areas expand. Urban forests change as trees are planted, grow, die, and are removed. These processes alter a city's tree cover over time, but this inherent dynamism is poorly understood. Better understanding of how tree cover is a variable land cover component will enhance knowledge of the urban environment and provide new perspectives for management of urban resources. In this study, tree cover variability within a major urban center was observed over a 20 year period. Changes in tree cover proportion were measured in the District of Columbia between 1984-2004 utilizing highly calibrated satellite remote sensing data. Testing of alternate methodologies demonstrated that an approach utilizing support vector regression provided most consistent accuracy across land use types. Tree cover maps were validated using aerial photography imagery and data from field surveys. Between 1984-2004, the city-wide tree cover remained between 22.1(+/-2.9)% and 28.8(+/-2.9)% of total land surface area. The District of Columbia did not experience an overall increase or decrease in total tree canopy area. Spatial patterns of tree cover variability were investigated to identify local scale changes in tree cover and connections with urban land use. Within the city, greatest variability was observed in low density residential zones. Tree cover proportion in these zones declined 7.4(+/-5.4)% in the years between 1990-1996 and recovered after 1996. Changes in tree cover were observed with high resolution aerial photography to determine relative contribution from fluctuation in the number of standing trees and changes in crown sizes. Land cover conversion removed dense tree cover from 50.2 hectares of the city's land surface between 1984-2004. The results demonstrate that tree cover variability in the District of Columbia occurred primarily within low population density residential areas. Neighborhoods within these zones were analyzed to identify factors correlated with tree cover. Implications of the results include enhanced understanding of the possible impact of urban forest management, and how a focus on low density residential zones is appropriate in setting goals for expansion of urban tree cover

    Remote Sensing of Land Surface Phenology

    Get PDF
    Land surface phenology (LSP) uses remote sensing to monitor seasonal dynamics in vegetated land surfaces and retrieve phenological metrics (transition dates, rate of change, annual integrals, etc.). LSP has developed rapidly in the last few decades. Both regional and global LSP products have been routinely generated and play prominent roles in modeling crop yield, ecological surveillance, identifying invasive species, modeling the terrestrial biosphere, and assessing impacts on urban and natural ecosystems. Recent advances in field and spaceborne sensor technologies, as well as data fusion techniques, have enabled novel LSP retrieval algorithms that refine retrievals at even higher spatiotemporal resolutions, providing new insights into ecosystem dynamics. Meanwhile, rigorous assessment of the uncertainties in LSP retrievals is ongoing, and efforts to reduce these uncertainties represent an active research area. Open source software and hardware are in development, and have greatly facilitated the use of LSP metrics by scientists outside the remote sensing community. This reprint covers the latest developments in sensor technologies, LSP retrieval algorithms and validation strategies, and the use of LSP products in a variety of fields. It aims to summarize the ongoing diverse LSP developments and boost discussions on future research prospects

    Crop modeling for assessing and mitigating the impacts of extreme climatic events on the US agriculture system

    Get PDF
    The US agriculture system is the worldโ€™s largest producer of maize and soybean, and typically supplies more than one-third of their global trading. Nearly 90% of the US maize and soybean production is rainfed, thus is susceptible to climate change stressors such as heat waves and droughts. Process-based crop and cropping system models are important tools for climate change impact assessments and risk management. As data- science is becoming a new frontier for agriculture growth, the incoming decade calls for operational platforms that use hyper-local growth monitoring, high-resolution real-time weather and satellite data assimilation and cropping system modeling to help stakeholders predict crop yields and make decisions at various spatial scales. The fundamental question addressed by this dissertation is: How crop and cropping system models can be โ€œusefulโ€ to the agriculture production, given the recent advent of cloud computing and earth observatory power? This dissertation consists of four main chapters. It starts with a study that reviews the algorithms of simulating heat and drought stress on maize in 16 major crop models, and evaluates algorithm performances by incorporating these algorithms into the Agricultural Production Systems sIMulator (APSIM) and running an ensemble of simulations at typical farms from the US Midwest. Results show that current parameterizations in most models favor the use of daylight temperature even though the algorithm was designed for using daily mean temperature. Different drought algorithms considerably differed in their patterns of water shortage over the growing season, but nonetheless predicted similar decreases in annual yield. In the next chapter of climate change assessment study, I quantify the current and future yield responses of US rainfed maize and soybean to climate extremes with and without considering the effect of elevated atmospheric CO2concentrations, and for the first time characterizes spatial shifts in the relative importance of temperature, heat and drought stresses. Model simulations demonstrate that drought will continue to be the largest threat to rainfed maize and soybean production, yet shifts in the spatial pattern of dominant stressors are characterized by increases in the concurrent stress, indicating future adaptation strategies will have trade-offs between multiple objectives. Following this chapter, I presented a chapter that uses billion-scale simulations to identify the optimal combination of Genotype ร— Environment ร— Management for the purpose of minimizing the negative impact of climate extremes on the rainfed maize yield. Finally, I present a prototype of crop model and satellite imagery based within-field scale N sidedress prescription tool for the US rainfed maize system. As an early attempt to integrate advances in multiple areas for precision agriculture, this tool successfully captures the subfield variability of N dynamics and gives reasonable spatially explicit sidedress N recommendations. The prescription enhances zones with high yield potentials, while prevents over-fertilization at zones with low yield potentials

    Thermal infrared dust optical depth and coarse-mode effective diameter retrieved from collocated MODIS and CALIOP observations

    Get PDF
    In this study, we developed a novel algorithm based on the collocated Moderate Resolution Imaging Spectroradiometer (MODIS) thermal infrared (TIR) observations and dust vertical profiles from the Cloud-Aerosol Lidar with Orthogonal Polarization (CALIOP) to simultaneously retrieve dust aerosol optical depth at 10 &micro;m (DAOD10&mu;m) and the coarse-mode dust effective diameter (Deff) over global oceans. The accuracy of the Deff retrieval is assessed by comparing retrieved Deff with the in-situ measured dust particle size distributions (PSDs) from the AER-D, SAMUM-2 and SALTRACE field campaigns through case studies. The new DAOD10&mu;m retrievals were evaluated first through comparisons with the collocated DAOD10.6&mu;m retrieved from the combined Imaging Infrared Radiometer (IIR) and CALIOP observations from our previous study (Zheng et al. 2022). The pixel-to-pixel comparison of the two retrievals indicates a good agreement (R~0.7) and a significant reduction of (~50 %) retrieval uncertainties largely thanks to the better constraint on dust size. In a climatological comparison, the seasonal and regional (5&deg;&times;2&deg;) mean DAOD10um retrievals based on our combined MODIS and CALIOP method are in good agreement with the two independent Infrared Atmospheric Sounding Interferometer (IASI) products over three dust transport regions (i.e., North Atlantic (NA; R = 0.9), Indian Ocean (IO; R = 0.8) and North Pacific (NP; R = 0.7)). Using the new retrievals from 2013 to 2017, we performed a climatological analysis of coarse mode dust Deff over global oceans. We found that dust Deff over IO and NP are up to 20 % smaller than that over NA. Over NA in summer, we found a ~50 % reduction of the number of retrievals with Deff &gt; 5 &mu;m from 15&deg; W to 35&deg; W and a stable trend of Deff average at 4.4 &mu;m from 35&deg; W throughout the Caribbean Sea (90&deg; W). Over NP in spring, only ~5 % of retrieved pixels with Deff &gt; 5 &mu;m are found from 150&deg; E to 180&deg;, while the mean Deff remains stable at 4.0 &mu;m throughout eastern NP. To our best knowledge, this study is the first to retrieve both DAOD and coarse-mode dust particle size over global oceans for multiple years. This retrieval dataset provides insightful information for evaluating dust long-wave radiative effects and coarse mode dust particle size in models.</p

    ๊ทผ์ ‘ ํ‘œ๋ฉด ์›๊ฒฉ ์„ผ์‹ฑ ์‹œ์Šคํ…œ๋“ค์„ ์ด์šฉํ•œ ์ง€์†์  ์‹๋ฌผ ๊ณ„์ ˆ ๋ฐ ํƒœ์–‘ ์œ ๋„ ์—ฝ๋ก์†Œ ํ˜•๊ด‘๋ฌผ์งˆ ๊ด€์ธก

    Get PDF
    ํ•™์œ„๋…ผ๋ฌธ(๋ฐ•์‚ฌ) -- ์„œ์šธ๋Œ€ํ•™๊ต๋Œ€ํ•™์› : ํ™˜๊ฒฝ๋Œ€ํ•™์› ํ˜‘๋™๊ณผ์ • ์กฐ๊ฒฝํ•™, 2022.2. ๋ฅ˜์˜๋ ฌ.Monitoring phenology, physiological and structural changes in vegetation is essential to understand feedbacks of vegetation between terrestrial ecosystems and the atmosphere by influencing the albedo, carbon flux, water flux and energy. To this end, normalized difference vegetation index (NDVI) and solar-induced chlorophyll fluorescence (SIF) from satellite remote sensing have been widely used. However, there are still limitations in satellite remote sensing as 1) satellite imagery could not capture fine-scale spatial resolution of SIF signals, 2) satellite products are strongly influenced by condition of the atmosphere (e.g. clouds), thus it is challenging to know physiological and structural changes in vegetation on cloudy days and 3) satellite imagery captured a mixed signal from over- and understory, thus it is difficult to study the difference between overstory and understory phenology separately. Therefore, in order to more accurately understand the signals observed from the satellite, further studies using near-surface remote sensing system to collect ground-based observed data are needed. The main purpose of this dissertation is continuous observation of vegetation phenology and SIF using near-surface remote sensing system. To achieve the main goal, I set three chapters as 1) developing low-cost filter-based near-surface remote sensing system to monitor SIF continuously, 2) monitoring SIF in a temperate evergreen needleleaf forest continuously, and 3) understanding the relationships between phenology from in-situ multi-layer canopies and satellite products. In Chapter 2, I developed the filter-based smart surface sensing system (4S-SIF) to overcome the technical challenges of monitoring SIF in the field as well as to decrease sensor cost for more comprehensive spatial sampling. I verified the satisfactory spectral performance of the bandpass filters and confirmed that digital numbers (DN) from 4S-SIF exhibited linear relationships with the DN from the hyperspectral spectroradiometer in each band (R2 > 0.99). In addition, we confirmed that 4S-SIF shows relatively low variation of dark current value at various temperatures. Furthermore, the SIF signal from 4S-SIF represents a strong linear relationship with QEpro-SIF either changing the physiological mechanisms of the plant using DCMU (3-(3, 4-dichlorophenyl)-1, 1-dimethyurea) treatment. I believe that 4S-SIF will be a useful tool for collecting in-situ data across multiple spatial and temporal scales. Satellite-based SIF provides us with new opportunities to understand the physiological and structural dynamics of vegetation from canopy to global scales. However, the relationships between SIF and gross primary productivity (GPP) are not fully understood, which is mainly due to the challenges of decoupling structural and physiological factors that control the relationships. In Chapter 3, I reported the results of continuous observations of canopy-level SIF, GPP, absorbed photosynthetically active radiation (APAR), and chlorophyll: carotenoid index (CCI) in a temperate evergreen needleleaf forest. To understand the mechanisms underlying the relationship between GPP and SIF, I investigated the relationships of light use efficiency (LUE_p), chlorophyll fluorescence yield (ฮฆ_F), and the fraction of emitted SIF photons escaping from the canopy (f_esc) separately. I found a strongly non-linear relationship between GPP and SIF at diurnal and seasonal time scales (R2 = 0.91 with a hyperbolic regression function, daily). GPP saturated with APAR, while SIF did not. In addition, there were differential responses of LUE_p and ฮฆ_F to air temperature. While LUE_p reached saturation at high air temperatures, ฮฆ_F did not saturate. I also found that the canopy-level chlorophyll: carotenoid index was strongly correlated to canopy-level ฮฆ_F (R2 = 0.84) implying that ฮฆ_F could be more closely related to pigment pool changes rather than LUE_p. In addition, I found that the f_esc contributed to a stronger SIF-GPP relationship by partially capturing the response of LUE_p to diffuse light. These findings can help refine physiological and structural links between canopy-level SIF and GPP in evergreen needleleaf forests. We do not fully understand what satellite NDVI derived leaf-out and full leaf dates actually observe because deciduous broadleaf forest consists of multi-layer canopies typically and mixed-signal from multi-layer canopies could affect satellite observation. Ultimately, we have the following question: What phenology do we actually see from space compared to ground observations on multi-layer canopy phenology? In Chapter 4, I reported the results of 8 years of continuous observations of multi-layer phenology and climate variables in a deciduous broadleaf forest, South Korea. Multi-channel spectrometers installed above and below overstory canopy allowed us to monitor over- and understory canopy phenology separately, continuously. I evaluated the widely used phenology detection methods, curvature change rate and threshold with NDVI observed above top of the canopy and compared leaf-out and full leaf dates from both methods to in-situ observed multi-layer phenology. First, I found that NDVI from the above canopy had a strong linear relationship with satellites NDVI (R2=0.95 for MODIS products and R2= 0.85 for Landsat8). Second, leaf-out dates extracted by the curvature change rate method and 10% threshold were well matched with understory leaf-out dates. Third, the full-leaf dates extracted by the curvature change rate method and 90% threshold were similar to overstory full-leaf dates. Furthermore, I found that overstory leaf-out dates were closely correlated to accumulated growing degree days (AGDD) while understory leaf-out dates were related to AGDD and also sensitive to the number of chill days (NCD). These results suggest that satellite-based leaf-out and full leaf dates represent understory and overstory signals in the deciduous forest site, which requires caution when using satellite-based phenology data into future prediction as overstory and understory canopy show different sensitivities to AGDD and NCD.์‹๋ฌผ ๊ณ„์ ˆ ๋ฐ ์‹์ƒ์˜ ์ƒ๋ฆฌํ•™์ , ๊ตฌ์กฐ์ ์ธ ๋ณ€ํ™”๋ฅผ ์ง€์†์ ์œผ๋กœ ๋ชจ๋‹ˆํ„ฐ๋ง ํ•˜๋Š” ๊ฒƒ์€ ์œก์ƒ์ƒํƒœ๊ณ„์™€ ๋Œ€๊ธฐ๊ถŒ ์‚ฌ์ด์˜ ์—๋„ˆ์ง€, ํƒ„์†Œ ์ˆœํ™˜ ๋“ฑ์˜ ํ”ผ๋“œ๋ฐฑ์„ ์ดํ•ดํ•˜๋Š”๋ฐ ํ•„์ˆ˜์ ์ด๋‹ค. ์ด๋ฅผ ๊ด€์ธกํ•˜๊ธฐ ์œ„ํ•˜์—ฌ ์œ„์„ฑ์—์„œ ๊ด€์ธก๋œ ์ •๊ทœํ™” ์‹์ƒ ์ง€์ˆ˜ (NDVI) ํƒœ์–‘ ์œ ๋„ ์—ฝ๋ก์†Œ ํ˜•๊ด‘๋ฌผ์งˆ (SIF)๋Š” ๋Œ€์ค‘์ ์œผ๋กœ ์‚ฌ์šฉ๋˜๊ณ  ์žˆ๋‹ค. ๊ทธ๋Ÿฌ๋‚˜, ์šฐ์ฃผ ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ ์ž๋ฃŒ๋Š” ๋‹ค์Œ๊ณผ ๊ฐ™์€ ํ•œ๊ณ„์ ๋“ค์ด ์กด์žฌํ•œ๋‹ค. 1) ์•„์ง๊นŒ์ง€ ๊ณ ํ•ด์ƒ๋„์˜ ์œ„์„ฑ ๊ธฐ๋ฐ˜ SIF ์ž๋ฃŒ๋Š” ์—†๊ณ , 2) ์œ„์„ฑ ์ž๋ฃŒ๋“ค์€ ๋Œ€๊ธฐ์˜ ์งˆ (์˜ˆ, ๊ตฌ๋ฆ„)์— ์˜ํ–ฅ์„ ๋ฐ›์•„, ํ๋ฆฐ ๋‚ ์˜ ์‹์ƒ์˜ ์ƒ๋ฆฌํ•™์ , ๊ตฌ์กฐ์  ๋ณ€ํ™”๋ฅผ ํƒ์ง€ํ•˜๊ธฐ ํž˜๋“ค๋‹ค. ๋˜ํ•œ, 3) ์œ„์„ฑ ์ด๋ฏธ์ง€๋Š” ์ƒ๋ถ€ ์‹์ƒ๊ณผ ํ•˜๋ถ€ ์‹์ƒ์ด ํ˜ผํ•ฉ๋˜์–ด ์„ž์ธ ์‹ ํ˜ธ๋ฅผ ํƒ์ง€ํ•˜๊ธฐ ๋•Œ๋ฌธ์—, ๊ฐ ์ธต์˜ ์‹๋ฌผ ๊ณ„์ ˆ์„ ๊ฐ๊ฐ ์—ฐ๊ตฌํ•˜๊ธฐ์— ์–ด๋ ค์›€์ด ์žˆ๋‹ค. ๊ทธ๋Ÿฌ๋ฏ€๋กœ, ์œ„์„ฑ์—์„œ ํƒ์ง€ํ•œ ์‹ ํ˜ธ๋ฅผ ํ‰๊ฐ€ํ•˜๊ณ , ์‹์ƒ์˜ ์ƒ๋ฆฌํ•™์ , ๊ตฌ์กฐ์  ๋ณ€ํ™”๋ฅผ ๋ณด๋‹ค ์ •ํ™•ํžˆ ์ดํ•ดํ•˜๊ธฐ ์œ„ํ•ด์„œ๋Š” ๊ทผ์ ‘ ํ‘œ๋ฉด ์›๊ฒฉ ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ์ด์šฉํ•œ ์‹ค์ธก ์ž๋ฃŒ ๊ธฐ๋ฐ˜์˜ ์—ฐ๊ตฌ๋“ค์ด ์š”๊ตฌ๋œ๋‹ค. ๋ณธ ํ•™์œ„๋…ผ๋ฌธ์˜ ์ฃผ ๋ชฉ์ ์€ ๊ทผ์ ‘ ํ‘œ๋ฉด ์›๊ฒฉ ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ์ด์šฉํ•˜์—ฌ ์‹๋ฌผ ๊ณ„์ ˆ ๋ฐ SIF๋ฅผ ํ˜„์žฅ์—์„œ ์ง€์†์ ์œผ๋กœ ์‹ค์ธกํ•˜๊ณ , ์œ„์„ฑ ์˜์ƒ ๊ธฐ๋ฐ˜์˜ ์—ฐ๊ตฌ๊ฐ€ ๊ฐ–๊ณ  ์žˆ๋Š” ํ•œ๊ณ„์  ๋ฐ ๊ถ๊ธˆ์ฆ๋“ค์„ ํ•ด๊ฒฐ ๋ฐ ๋ณด์™„ํ•˜๋Š” ๊ฒƒ์ด๋‹ค. ์ด ๋ชฉ์ ์„ ๋‹ฌ์„ฑํ•˜๊ธฐ ์œ„ํ•˜์—ฌ, ์•„๋ž˜์™€ ๊ฐ™์€ ์„ธ๊ฐ€์ง€ Chapter: 1) SIF๋ฅผ ๊ด€์ธกํ•˜๊ธฐ ์œ„ํ•œ ํ•„ํ„ฐ ๊ธฐ๋ฐ˜์˜ ์ €๋ ดํ•œ ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ ์‹œ์Šคํ…œ ๊ฐœ๋ฐœ, 2)์˜จ๋Œ€ ์นจ์—ฝ์ˆ˜๋ฆผ์—์„œ์˜ ์—ฐ์†์ ์ธ SIF ๊ด€์ธก, 3)์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ ์‹๋ฌผ ๊ณ„์ ˆ๊ณผ ์‹ค์ธกํ•œ ๋‹ค์ธต ์‹์ƒ์˜ ์‹๋ฌผ ๊ณ„์ ˆ ๋น„๊ต๋กœ ๊ตฌ์„ฑํ•˜๊ณ , ์ด๋ฅผ ์ง„ํ–‰ํ•˜์˜€๋‹ค. SIF๋Š” ์‹์ƒ์˜ ๊ตฌ์กฐ์ , ์ƒ๋ฆฌํ•™์  ๋ณ€ํ™”๋ฅผ ์ดํ•ดํ•˜๊ณ , ์ถ”์ •ํ•˜๋Š” ์ธ์ž๋กœ ์‚ฌ์šฉ๋  ์ˆ˜ ์žˆ์–ด, SIF๋ฅผ ํ˜„์žฅ์—์„œ ๊ด€์ธกํ•˜๊ธฐ ์œ„ํ•œ ๋‹ค์–‘ํ•œ ๊ทผ์ ‘ ํ‘œ๋ฉด ์›๊ฒฉ ์„ผ์‹ฑ ์‹œ์Šคํ…œ๋“ค์ด ์ตœ๊ทผ ์ œ์‹œ๋˜์–ด ์˜ค๊ณ  ์žˆ๋‹ค. ๊ทธ๋Ÿฌ๋‚˜, ์•„์ง๊นŒ์ง€ SIF๋ฅผ ๊ด€์ธกํ•˜๊ธฐ ์œ„ํ•œ ์ƒ์—…์ ์œผ๋กœ ์œ ํ†ต๋˜๋Š” ๊ด€์ธก ์‹œ์Šคํ…œ์€ ํ˜„์ €ํžˆ ๋ถ€์กฑํ•˜๋ฉฐ, ๋ถ„๊ด‘๊ณ„์˜ ๊ตฌ์กฐ์  ํŠน์„ฑ์ƒ ํ˜„์žฅ์—์„œ ๊ด€์ธก ์‹œ์Šคํ…œ์„ ๋ณด์ • ๋ฐ ๊ด€๋ฆฌํ•˜๊ธฐ๊ฐ€ ์–ด๋ ค์›Œ ๋†’์€ ์งˆ์˜ SIF๋ฅผ ์ทจ๋“ํ•˜๋Š” ๊ฒƒ์€ ๋งค์šฐ ๋„์ „ ์ ์ธ ๋ถ„์•ผ์ด๋‹ค. ๋ณธ ํ•™์œ„ ๋…ผ๋ฌธ์˜ Chapter 2์—์„œ๋Š” SIF๋ฅผ ํ˜„์žฅ์—์„œ ๋ณด๋‹ค ์†์‰ฝ๊ฒŒ ๊ด€์ธกํ•˜๊ธฐ ์œ„ํ•œ ํ•„ํ„ฐ ๊ธฐ๋ฐ˜์˜ ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ ์‹œ์Šคํ…œ(Smart Surface Sensing System, 4S-SIF)์„ ๊ฐœ๋ฐœํ•˜์˜€๋‹ค. ์„ผ์„œ๋Š” ๋Œ€์—ญ ํ•„ํ„ฐ๋“ค๊ณผ ํฌํ† ๋‹ค์ด์˜ค๋“œ๊ฐ€ ๊ฒฐํ•ฉ๋˜์–ด ์žˆ์œผ๋ฉฐ, ์„œ๋ณด ๋ชจํ„ฐ๋ฅผ ์‚ฌ์šฉํ•˜์—ฌ ๋Œ€์—ญ ํ•„ํ„ฐ ๋ฐ ๊ด€์ธก ๋ฐฉํ–ฅ์„ ์ž๋™์ ์œผ๋กœ ๋ณ€๊ฒฝํ•จ์œผ๋กœ์จ, ํ•œ ๊ฐœ์˜ ํฌํ† ๋‹ค์ด์˜ค๋“œ๊ฐ€ 3๊ฐœ์˜ ํŒŒ์žฅ ๋ฒ”์œ„(757, 760, 770 nm)์˜ ๋น› ๋ฐ ํƒœ์–‘์œผ๋กœ๋ถ€ํ„ฐ ์ž…์‚ฌ๋˜๋Š” ๊ด‘๋Ÿ‰๊ณผ ์‹์ƒ์œผ๋กœ ๋ฐ˜์‚ฌ/๋ฐฉ์ถœ๋œ ๊ด‘๋Ÿ‰์„ ๊ด€์ธกํ•  ์ˆ˜ ์žˆ๋„๋ก ๊ณ ์•ˆ๋˜์—ˆ๋‹ค. ํฌํ† ๋‹ค์ด์˜ค๋“œ๋กœ๋ถ€ํ„ฐ ์ธ์‹๋œ ๋””์ง€ํ„ธ ์ˆ˜์น˜ ๊ฐ’์€ ์ƒ์—…์ ์œผ๋กœ ํŒ๋งค๋˜๋Š” ์ดˆ๊ณ ํ•ด์ƒ๋„ ๋ถ„๊ด‘๊ณ„(QE Pro, Ocean Insight)์™€ ๋šœ๋ ทํ•œ ์„ ํ˜• ๊ด€๊ณ„๋ฅผ ๋ณด์ด๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค (R2 > 0.99). ์ถ”๊ฐ€์ ์œผ๋กœ, 4S-SIF์—์„œ ๊ด€์ธก๋œ SIF์™€ ์ดˆ๊ณ ํ•ด์ƒ๋„ ๋ถ„๊ด‘๊ณ„๋ฅผ ์ด์šฉํ•˜์—ฌ ์ถ”์ถœํ•œ SIF๊ฐ€ ์„ ํ˜•์ ์ธ ๊ด€๊ณ„๋ฅผ ์ด๋ฃจ๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ์‹์ƒ์˜ ์ƒ๋ฆฌํ•™์  ๋ณ€ํ™”๋ฅผ ์ผ์œผํ‚ค๋Š” ํ™”ํ•™ ๋ฌผ์งˆ์ธ DCMU(3-(3, 4-dichlorophenyl)-1, 1-dimethyurea)์„ ์ฒ˜๋ฆฌํ–ˆ์Œ์—๋„ ๋ถˆ๊ตฌํ•˜๊ณ , ์‚ฐ์ถœ๋œ SIF๋“ค์€ ์„ ํ˜• ๊ด€๊ณ„๋ฅผ ๋ณด์˜€๋‹ค. ๋ณธ ์„ผ์„œ๋Š” ๊ธฐ์กด ์‹œ์Šคํ…œ๋“ค์— ๋น„ํ•ด ์‚ฌ์šฉํ•˜๊ธฐ ์‰ฝ๊ณ  ๊ฐ„๋‹จํ•˜๋ฉฐ, ์ €๋ ดํ•˜๊ธฐ ๋•Œ๋ฌธ์— ๋‹ค์–‘ํ•œ ์‹œ๊ณต๊ฐ„์  ์Šค์ผ€์ผ์˜ SIF๋ฅผ ๊ด€์ธกํ•  ์ˆ˜ ์žˆ๋‹ค๋Š” ์žฅ์ ์ด ์žˆ๋‹ค. ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ SIF๋ฅผ ์ด์šฉํ•˜์—ฌ ์ด์ผ์ฐจ์ƒ์‚ฐ์„ฑ(gross primary productivity, GPP)์„ ์ถ”์ •ํ•˜๋Š” ์—ฐ๊ตฌ๋Š” ์ตœ๊ทผ ํƒ„์†Œ ์ˆœํ™˜ ์—ฐ๊ตฌ ๋ถ„์•ผ์—์„œ ๊ฐ๊ด‘๋ฐ›๊ณ  ์žˆ๋Š” ์—ฐ๊ตฌ ์ฃผ์ œ์ด๋‹ค. ๊ทธ๋Ÿฌ๋‚˜, SIF์™€ GPP์˜ ๊ด€๊ณ„๋Š” ์—ฌ์ „ํžˆ ๋งŽ์€ ๋ถˆํ™•์‹ค์„ฑ์„ ์ง€๋‹ˆ๊ณ  ์žˆ๋Š”๋ฐ, ์ด๋Š” SIF-GPP ๊ด€๊ณ„๋ฅผ ์กฐ์ ˆํ•˜๋Š” ์‹์ƒ์˜ ๊ตฌ์กฐ์  ๋ฐ ์ƒ๋ฆฌํ•™์  ์š”์ธ์„ ๋”ฐ๋กœ ๋ถ„๋ฆฌํ•˜์—ฌ ๊ณ ์ฐฐํ•œ ์—ฐ๊ตฌ๋“ค์ด ๋ถ€์กฑํ•˜๊ธฐ ๋•Œ๋ฌธ์ด๋‹ค. ๋ณธ ํ•™์œ„ ๋…ผ๋ฌธ์˜ Chapter 3์—์„œ๋Š” ์ง€์†์ ์œผ๋กœ SIF, GPP, ํก์ˆ˜๋œ ๊ด‘ํ•ฉ์„ฑ์œ ํšจ๋ณต์‚ฌ๋Ÿ‰ (absorbed photosynthetically active radiation, APAR), ๊ทธ๋ฆฌ๊ณ  ํด๋กœ๋กœํ•„๊ณผ ์นด๋กœํ‹ฐ๋…ธ์ด๋“œ์˜ ๋น„์œจ ์ธ์ž (chlorophyll: carotenoid index, CCI)๋ฅผ ์˜จ๋Œ€์นจ์—ฝ์ˆ˜๋ฆผ์—์„œ ์—ฐ์†์ ์œผ๋กœ ๊ด€์ธกํ•˜์˜€๋‹ค. SIF-GPP ๊ด€๊ณ„์˜ ๊ตฌ์ฒด์ ์ธ ๋ฉ”์ปค๋‹ˆ์ฆ˜ ๊ด€๊ณ„๋ฅผ ๋ฐํžˆ๊ธฐ ์œ„ํ•˜์—ฌ, ๊ด‘ ์ด์šฉํšจ์œจ (light use efficiency, LUE_p), ์—ฝ๋ก์†Œ ํ˜•๊ด‘ ์ˆ˜๋“๋ฅ  (chlorophyll fluorescence yield, ฮฆ_F) ๊ทธ๋ฆฌ๊ณ  SIF ๊ด‘์ž๊ฐ€ ๊ตฐ๋ฝ์œผ๋กœ๋ถ€ํ„ฐ ๋ฐฉ์ถœ๋˜๋Š” ๋น„์œจ (escape fraction, f_esc)์„ ๊ฐ๊ฐ ๋„์ถœํ•˜๊ณ  ํƒ๊ตฌํ•˜์˜€๋‹ค. SIF์™€ GPP์˜ ๊ด€๊ณ„๋Š” ๋šœ๋ ทํ•œ ๋น„ ์„ ํ˜•์ ์ธ ๊ด€๊ณ„๋ฅผ ๋ณด์ด๋Š” ๊ฒƒ์„ ํ™•์ธํ–ˆ์œผ๋ฉฐ(R2 = 0.91 with a hyperbolic regression function, daily), ์ผ์ฃผ๊ธฐ ๋‹จ์œ„์—์„œ SIF๋Š” APAR์— ๋Œ€ํ•ด ์„ ํ˜•์ ์ด์—ˆ์ง€๋งŒ GPP๋Š” APAR์— ๋Œ€ํ•ด ๋šœ๋ ทํ•œ ํฌํ™” ๊ด€๊ณ„๋ฅผ ๋ณด์ด๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ์ถ”๊ฐ€์ ์œผ๋กœ LUE_p ์™€ ฮฆ_F ๊ฐ€ ๋Œ€๊ธฐ ์˜จ๋„์— ๋”ฐ๋ผ ๋ฐ˜์‘ํ•˜๋Š” ์ •๋„๊ฐ€ ๋‹ค๋ฅธ ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. LUE_p๋Š” ๋†’์€ ์˜จ๋„์—์„œ ํฌํ™” ๋˜์—ˆ์ง€๋งŒ, ฮฆ_F๋Š” ํฌํ™” ํŒจํ„ด์„ ํ™•์ธํ•  ์ˆ˜ ์—†์—ˆ๋‹ค. ๋˜ํ•œ, ๊ตฐ๋ฝ ์ˆ˜์ค€์—์„œ์˜ CCI์™€ ฮฆ_F๊ฐ€ ๋šœ๋ ทํ•œ ์ƒ๊ด€ ๊ด€๊ณ„๋ฅผ ๋ณด์˜€๋‹ค(R2 = 0.84). ์ด๋Š” ฮฆ_F๊ฐ€ ์—ฝ๋ก์†Œ ์ƒ‰์†Œ์— ์˜ํ–ฅ์„ LUE_p์— ๋น„ํ•ด ๋” ๊ฐ•ํ•œ ๊ด€๊ณ„๊ฐ€ ์žˆ์„ ์ˆ˜ ์žˆ์Œ์„ ์‹œ์‚ฌํ•œ๋‹ค. ๋งˆ์ง€๋ง‰์œผ๋กœ, f_esc๊ฐ€ ํƒœ์–‘๊ด‘์˜ ์‚ฐ๋ž€๋œ ์ •๋„์— ๋”ฐ๋ผ ๋ฐ˜์‘์„ ํ•˜์—ฌ, ฮฆ_F์™€ LUE_p์˜ ๊ฐ•ํ•œ ์ƒ๊ด€ ๊ด€๊ณ„๋ฅผ ํ˜•์„ฑํ•˜๋Š”๋ฐ ๊ธฐ์—ฌํ•˜๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ์ด๋Ÿฌํ•œ ๋ฐœ๊ฒฌ์€ ์˜จ๋Œ€ ์นจ์—ฝ์ˆ˜๋ฆผ์—์„œ ๊ตฐ๋ฝ ์ˆ˜์ค€์˜ SIF-GPP๊ด€๊ณ„๋ฅผ ์ƒ๋ฆฌํ•™์  ๋ฐ ๊ตฌ์กฐ์  ์ธก๋ฉด์—์„œ ์ดํ•ดํ•˜๊ณ  ๊ทœ๋ช…ํ•˜๋Š”๋ฐ ํฐ ๋„์›€์ด ๋  ๊ฒƒ์ด๋‹ค. ์‹๋ฌผ ๊ณ„์ ˆ์€ ์‹์ƒ์ด ์ฒ ์„ ๋”ฐ๋ผ ์ฃผ๊ธฐ์ ์œผ๋กœ ๋‚˜ํƒ€๋‚ด๋Š” ๋ณ€ํ™”๋ฅผ ๊ด€์ธกํ•˜๋Š” ๋ฐ˜์‘์ด๋‹ค. ์‹๋ฌผ ๊ณ„์ ˆ์€ ์œก์ƒ์ƒํƒœ๊ณ„์™€ ๋Œ€๊ธฐ๊ถŒ ์‚ฌ์ด์˜ ๋ฌผ์งˆ ์ˆœํ™˜์„ ์ดํ•ดํ•˜๋Š”๋ฐ ๋งค์šฐ ์ค‘์š”ํ•˜๋‹ค. ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ NDVI๋Š” ์‹๋ฌผ ๊ณ„์ ˆ์„ ํƒ์ง€ํ•˜๊ณ  ์—ฐ๊ตฌํ•˜๋Š”๋ฐ ๊ฐ€์žฅ ๋Œ€์ค‘์ ์œผ๋กœ ์‚ฌ์šฉ๋œ๋‹ค. ๊ทธ๋Ÿฌ๋‚˜, ํ™œ์—ฝ์ˆ˜๋ฆผ์—์„œ์˜ ์œ„์„ฑ NDVI ๊ธฐ๋ฐ˜์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ ๋ฐ ์„ฑ์ˆ™ ์‹œ๊ธฐ๊ฐ€ ์‹ค์ œ ์–ด๋Š ์‹œ์ ์„ ํƒ์ง€ํ•˜๋Š”์ง€๋Š” ๋ถˆ๋ถ„๋ช…ํ•˜๋‹ค. ์‹ค์ œ ํ™œ์—ฝ์ˆ˜๋ฆผ์€ ๋‹ค์ธต ์‹์ƒ ๊ตฌ์กฐ์˜ ์‚ผ์ฐจ์›์œผ๋กœ ์ด๋ฃจ์–ด์ ธ ์žˆ๋Š” ๋ฐ˜๋ฉด, ์œ„์„ฑ ์˜์ƒ์€ ๋‹ค์ธต ์‹์ƒ์˜ ์‹ ํ˜ธ๊ฐ€ ์„ž์—ฌ ์žˆ๋Š” ์ด์ฐจ์›์˜ ๊ฒฐ๊ณผ๋ฌผ์ด๊ธฐ ๋•Œ๋ฌธ์ด๋‹ค. ๋”ฐ๋ผ์„œ, ์œ„์„ฑ NDVI ๊ธฐ๋ฐ˜์˜ ์‹๋ฌผ ๊ณ„์ ˆ์ด ๋‹ค์ธต ์‹์ƒ ๊ตฌ์กฐ๋ฅผ ์ด๋ฃจ๊ณ  ์žˆ๋Š” ํ™œ์—ฝ์ˆ˜๋ฆผ์—์„œ ์‹ค์ œ ํ˜„์žฅ ๊ด€์ธก๊ณผ ๋น„๊ตํ•˜์˜€์„ ๋•Œ ์–ด๋Š ์‹œ์ ์„ ํƒ์ง€ํ•˜๋Š”์ง€์— ๋Œ€ํ•œ ๊ถ๊ธˆ์ฆ์ด ๋‚จ๋Š”๋‹ค. ๋ณธ ํ•™์œ„ ๋…ผ๋ฌธ์˜ Chapter 4์—์„œ๋Š” ์ง€์†์ ์œผ๋กœ 8๋…„ ๋™์•ˆ ํ™œ์—ฝ์ˆ˜๋ฆผ๋‚ด์˜ ๋‹ค์ธต ์‹์ƒ์˜ ์‹๋ฌผ ๊ณ„์ ˆ์„ ๊ทผ์ ‘ ํ‘œ๋ฉด ์›๊ฒฉ ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ์ด์šฉํ•˜์—ฌ ๊ด€์ธกํ•˜๊ณ , ์œ„์„ฑ NDVI ๊ธฐ๋ฐ˜์˜ ์‹๋ฌผ ๊ณ„์ ˆ๊ณผ ๋น„๊ตํ•˜์˜€๋‹ค. ๋‹ค์ฑ„๋„ ๋ถ„๊ด‘๊ณ„๋ฅผ ์ƒ๋ถ€ ์‹์ƒ์˜ ์œ„์™€ ์•„๋ž˜์— ์„ค์น˜ํ•จ์œผ๋กœ์จ, ์ƒ๋ถ€ ์‹์ƒ๊ณผ ํ•˜๋ถ€ ์‹์ƒ์˜ ์‹๋ฌผ ๊ณ„์ ˆ์„ ๊ฐ๊ฐ ์—ฐ์†์ ์œผ๋กœ ๊ด€์ธกํ•˜์˜€๋‹ค. ์‹๋ฌผ ๊ณ„์ ˆ์„ ํƒ์ง€ํ•˜๊ธฐ ์œ„ํ•˜์—ฌ ๊ฐ€์žฅ ๋งŽ์ด ์‚ฌ์šฉ๋˜๋Š” ๋ฐฉ๋ฒ•์ธ 1) ์—ญ์น˜๋ฅผ ์ด์šฉํ•˜๋Š” ๋ฐฉ๋ฒ•๊ณผ 2) ์ด๊ณ„๋„ํ•จ์ˆ˜๋ฅผ ์ด์šฉํ•˜๋Š” ๋ฐฉ๋ฒ•์„ ์‚ฌ์šฉํ•˜์—ฌ ๊ฐœ์—ฝ ์‹œ๊ธฐ ๋ฐ ์„ฑ์ˆ™ ์‹œ๊ธฐ๋ฅผ ๊ณ„์‚ฐํ•˜๊ณ  ์ด๋ฅผ ๋‹ค์ธต ์‹์ƒ์˜ ์‹๋ฌผ ๊ณ„์ ˆ๊ณผ ๋น„๊ตํ•˜์˜€๋‹ค. ๋ณธ ์—ฐ๊ตฌ ๊ฒฐ๊ณผ, ์ฒซ๋ฒˆ์งธ๋กœ, ๊ตฐ๋ฝ์˜ ์ƒ์ธต๋ถ€์—์„œ ์‹ค์ธกํ•œ NDVI์™€ ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ NDVI๊ฐ€ ๊ฐ•ํ•œ ์„ ํ˜• ๊ด€๊ณ„๋ฅผ ๋ณด์ด๋Š” ๊ฒƒ์„ ํ™•์ธํ–ˆ๋‹ค (R2=0.95 ๋Š” MODIS ์˜์ƒ๋“ค ๋ฐ R2= 0.85 ๋Š” Landsat8). ๋‘๋ฒˆ์งธ๋กœ, ์ด๊ณ„๋„ํ•จ์ˆ˜ ๋ฐฉ๋ฒ•๊ณผ 10%์˜ ์—ญ์น˜ ๊ฐ’์„ ์ด์šฉํ•œ ๋ฐฉ๋ฒ•์ด ๋น„์Šทํ•œ ๊ฐœ์—ฝ ์‹œ๊ธฐ๋ฅผ ์ถ”์ •ํ•˜๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€์œผ๋ฉฐ, ํ•˜๋ถ€ ์‹์ƒ์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ์™€ ๋น„์Šทํ•œ ์‹œ๊ธฐ์ž„์„ ํ™•์ธํ•˜์˜€๋‹ค. ์„ธ๋ฒˆ์งธ๋กœ, ์ด๊ณ„๋„ํ•จ์ˆ˜ ๋ฐฉ๋ฒ•๊ณผ 90%์˜ ์—ญ์น˜ ๊ฐ’์„ ์ด์šฉํ•œ ๋ฐฉ๋ฒ•์ด ๋น„์Šทํ•œ ์„ฑ์ˆ™ ์‹œ๊ธฐ๋ฅผ ์‚ฐ์ถœํ•˜์˜€์œผ๋ฉฐ, ์ด๋Š” ์ƒ๋ถ€ ์‹์ƒ์˜ ์„ฑ์ˆ™ ์‹œ๊ธฐ์™€ ๋น„์Šทํ•˜์˜€๋‹ค. ์ถ”๊ฐ€์ ์œผ๋กœ ์ƒ๋ถ€ ์‹์ƒ์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ์™€ ํ•˜๋ถ€ ์‹์ƒ์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ๊ฐ€ ์˜จ๋„์™€ ๋ฐ˜์‘ํ•˜๋Š” ์ •๋„๊ฐ€ ๋šœ๋ ทํ•˜๊ฒŒ ์ฐจ์ด๊ฐ€ ๋‚˜๋Š” ๊ฒƒ์„ ํ™•์ธํ•  ์ˆ˜ ์žˆ์—ˆ๋‹ค. ์ƒ๋ถ€ ์‹์ƒ์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ๋Š” ์ ์‚ฐ ์ƒ์žฅ ์˜จ๋„ ์ผ์ˆ˜ (AGDD)์™€ ๊ฐ•ํ•œ ์ƒ๊ด€์„ฑ์„ ๋ณด์˜€๊ณ , ํ•˜๋ถ€ ์‹์ƒ์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ๋Š” AGDD์™€ ์—ฐ๊ด€์„ฑ์„ ๊ฐ–๊ณ  ์žˆ์„ ๋ฟ๋งŒ ์•„๋‹ˆ๋ผ ์ถ”์œ„ ์ผ์ˆ˜(NCD)์—๋„ ๋ฏผ๊ฐํ•˜๊ฒŒ ๋ฐ˜์‘ํ•˜๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ์ด๋Ÿฌํ•œ ๊ฒฐ๊ณผ๋Š” ์œ„์„ฑ NDVI ๊ธฐ๋ฐ˜์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ๋Š” ํ•˜๋ถ€ ์‹์ƒ์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ์™€ ์—ฐ๊ด€์„ฑ์ด ๋†’๊ณ , ์„ฑ์ˆ™ ์‹œ๊ธฐ๋Š” ์ƒ๋ถ€ ์‹์ƒ์˜ ์„ฑ์ˆ™ ์‹œ๊ธฐ์™€ ๋น„์Šทํ•˜๋‹ค๋Š” ๊ฒƒ์„ ์˜๋ฏธํ•œ๋‹ค. ๋˜ํ•œ, ์ƒ๋ถ€ ์‹์ƒ๊ณผ ํ•˜๋ถ€ ์‹์ƒ์ด ์˜จ๋„์— ๋‹ค๋ฅธ ๋ฏผ๊ฐ์„ฑ์„ ๊ฐ–๊ณ  ์žˆ์–ด, ์œ„์„ฑ์—์„œ ์‚ฐ์ถœ๋œ ์‹๋ฌผ ๊ณ„์ ˆ์„ ์ด์šฉํ•˜์—ฌ ๊ธฐํ›„๋ณ€ํ™”๋ฅผ ์ดํ•ดํ•˜๊ณ ์ž ํ•  ๋•Œ, ์–ด๋–ค ์ธต์˜ ์‹์ƒ์ด ์œ„์„ฑ ์˜์ƒ์— ์ฃผ๋œ ์˜ํ–ฅ์„ ๋ฏธ์น˜๋Š”์ง€ ๊ณ ๋ คํ•ด์•ผ ํ•œ๋‹ค๋Š” ๊ฒƒ์„ ์‹œ์‚ฌํ•œ๋‹ค. ์œ„์„ฑ์€ ๋„“์€ ์ง€์—ญ์˜ ๋ณ€ํ™”๋ฅผ ์†์‰ฝ๊ฒŒ ๋ชจ๋‹ˆํ„ฐ๋งํ•  ์ˆ˜ ์žˆ์–ด ๋งŽ์€ ๊ฐ€๋Šฅ์„ฑ์„ ๊ฐ–๊ณ  ์žˆ๋Š” ๋„๊ตฌ์ด์ง€๋งŒ, ๋ณด๋‹ค ์ •ํ™•ํ•œ ์œ„์„ฑ ๊ด€์ธก ๊ฐ’์„ ์ดํ•ดํ•˜๊ธฐ ์œ„ํ•ด์„œ๋Š” ํ˜„์žฅ์—์„œ ๊ด€์ธก๋œ ์ž๋ฃŒ๋ฅผ ๊ธฐ๋ฐ˜์œผ๋กœ ํ•œ ๊ฒ€์ฆ์ด ์š”๊ตฌ๋œ๋‹ค. ๋ณธ ํ•™์œ„ ๋…ผ๋ฌธ์—์„œ๋Š” 1) ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ๊ฐœ๋ฐœ, 2) ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ํ™œ์šฉํ•œ ์‹์ƒ์˜ ์ƒ๋ฆฌํ•™์  ๊ตฌ์กฐ์  ๋ณ€ํ™”์˜ ์ง€์†์ ์ธ ๊ด€์ธก, 3) ๋‹ค์ธต ์‹์ƒ ๊ตฌ์กฐ์—์„œ ๊ด€์ธก๋˜๋Š” ์‹๋ฌผ ๊ณ„์ ˆ ๋ฐ ์œ„์„ฑ์—์„œ ์ถ”์ •๋œ ์‹๋ฌผ ๊ณ„์ ˆ์˜ ์—ฐ๊ด€์„ฑ ํ‰๊ฐ€๋ฅผ ์ˆ˜ํ–‰ํ•˜์˜€๋‹ค. ๊ฐœ๋ฐœํ•œ ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์„œ๋Š” ์ƒ์—… ์„ผ์„œ๋“ค๊ณผ ๋น„๊ตํ–ˆ์„ ๋•Œ, ๊ฐ€๊ฒฉ์ ์œผ๋กœ ์ €๋ ดํ•˜๊ณ  ์† ์‰ฝ๊ฒŒ ์‚ฌ์šฉํ•  ์ˆ˜ ์žˆ์—ˆ์œผ๋ฉฐ, ์„ฑ๋Šฅ์ ์œผ๋กœ๋„ ๋ถ€์กฑํ•จ์ด ์—†์—ˆ๋‹ค. ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ์ด์šฉํ•˜์—ฌ SIF๋ฅผ ์˜จ๋Œ€ ์นจ์—ฝ์ˆ˜๋ฆผ์—์„œ ์ง€์†์ ์œผ๋กœ ๊ด€์ธกํ•œ ๊ฒฐ๊ณผ, ์ด์ผ์ฐจ์ƒ์‚ฐ์„ฑ๊ณผ SIF๋Š” ๋น„์„ ํ˜• ๊ด€๊ณ„๋ฅผ ๊ฐ–๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ์ด๋Š” ๋งŽ์€ ์„ ํ–‰ ์—ฐ๊ตฌ๋“ค์—์„œ ๋ฐœํ‘œํ•œ ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ SIF์™€ GPP๊ฐ€ ์„ ํ˜•์ ์ธ ๊ด€๊ณ„๋ฅผ ๋ณด์ธ๋‹ค๋Š” ๊ฒƒ๊ณผ๋Š” ๋‹ค์†Œ ์ƒ๋ฐ˜๋œ ๊ฒฐ๊ณผ์ด๋‹ค. ๋‹ค์ธก ์‹์ƒ์˜ ๋ด„์ฒ  ์‹๋ฌผ ๊ณ„์ ˆ์„ ์—ฐ์†์ ์œผ๋กœ ๊ด€์ธกํ•˜๊ณ , ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ ์‹๋ฌผ ๊ณ„์ ˆ๊ณผ ๋น„๊ตํ‰๊ฐ€ํ•œ ์—ฐ๊ตฌ์—์„œ๋Š” ์œ„์„ฑ ๊ธฐ๋ฐ˜์˜ ๊ฐœ์—ฝ ์‹œ๊ธฐ๋Š” ํ•˜๋ถ€ ์‹์ƒ์— ์˜ํ–ฅ์„ ์ฃผ๋กœ ๋ฐ›๊ณ , ์„ฑ์ˆ™ ์‹œ๊ธฐ๋Š” ์ƒ๋ถ€ ์‹์ƒ์˜ ์‹œ๊ธฐ์™€ ๋น„์Šทํ•œ ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ์ฆ‰, ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ ์‹œ์Šคํ…œ์„ ์ด์šฉํ•˜์—ฌ ํ˜„์žฅ์—์„œ ์‹ค์ธกํ•œ ๊ฒฐ๊ณผ๋Š” ์œ„์„ฑ ์˜์ƒ์„ ํ™œ์šฉํ•œ ์—ฐ๊ตฌ๋“ค๊ณผ๋Š” ๋‹ค๋ฅธ ๊ฒฐ๊ณผ๋ฅผ ๋ณด์ผ ์ˆ˜๋„ ์žˆ์œผ๋ฉฐ, ์œ„์„ฑ ์˜์ƒ์„ ํ‰๊ฐ€ ๋ฐ ์ดํ•ดํ•˜๋Š”๋ฐ ์‚ฌ์šฉ๋  ์ˆ˜ ์žˆ๋‹ค. ๋”ฐ๋ผ์„œ, ๋ณด๋‹ค ์ •ํ™•ํ•œ ์‹์ƒ์˜ ๊ตฌ์กฐ์ , ์ƒ๋ฆฌํ•™์  ๋ฉ”์ปค๋‹ˆ์ฆ˜์„ ์ดํ•ดํ•˜๊ธฐ ์œ„ํ•ด์„œ๋Š” ๊ทผ์ ‘ ํ‘œ๋ฉด ์„ผ์‹ฑ์„ ํ™œ์šฉํ•œ ํ˜„์žฅ์—์„œ ๊ตฌ์ถ•ํ•œ ์ž๋ฃŒ ๊ธฐ๋ฐ˜์˜ ๋” ๋งŽ์€ ์—ฐ๊ตฌ๋“ค์ด ํ•„์š”ํ•˜๋‹ค๋Š” ๊ฒƒ์„ ์‹œ์‚ฌํ•œ๋‹ค.Abstract i Chapter 1. Introduction 2 1. Background 2 2. Purpose 5 Chapter 2. Monitoring SIF using a filter-based near surface remote sensing system 9 1. Introduction 9 2. Instrument desing and technical spefications of the filter-based smart surface sensing system (4S-SIF) 12 2.1. Ultra-narrow band pass filter 14 2.2. Calibration of 4S-SIF 15 2.3. Temperature and humidity response 16 2.4. Evaluate SIF quality from 4S-SIF in the field 17 3. Results 20 4. Discussion 23 Chapter 3. SIF is non-linearly related to canopy photosynthesis in a temperate evergreen needleleaf forest during fall transition 27 1. Introduction 27 2. Methods and Materials 31 2.1. Study site 31 2.2. Leaf-level fluorescence measurement 32 2.3. Canopy-level SIF and spectral reflectance measurement 34 2.4. SIF retrieval 37 2.5. Canopy-level photosynthesis estimates 38 2.6. Meteorological variables and APAR 39 2.7. Statistical analysis 40 3. Results 41 4. Discussion 48 4.1. Non-linear relationships between SIF and GPP 49 4.2. Role of f_esc in SIF-GPP relationship 53 4.3. Implications of non-linear SIF-GPP relationship in temperate ENF 54 5. Conclusion 57 6. Appendix 59 Chapter 4. Monitoring spring phenology of multi-layer canopy in a deciduous broadleaf forest: What signal do satellites actually see in space 65 1. Introduction 65 2. Materials and Methods 69 2.1. Study site 69 2.2. Multi-layer spectral reflectance and transmittance measurement 70 2.3. Phenometrics detection 72 2.4. In-situ multi-layer phenology 74 2.5. Satellite remote sensing data 75 2.6. Meteorological variables 75 3. Results 76 3.1. Seasonal to interannual variations of NDVI, 1-transmittance, and air temperature 76 3.2. Inter-annual variation of leaf-out and full-leaf dates 78 3.3. The relationships between dates calculated according tothreshold and in-situ multi-layer phenology 80 3.4. The relationship between multi-layer phenology, AGDD and NCD 81 4. Discussion 82 4.1. How do satellite-based leaf-out and full-leaf dates differ from in-situ multi-layer phenology 83 4.2. Are the 10 % and 90 % thresholds from satellite-basedNDVI always well matched with the leaf-out and full-leaf dates calculated by the curvature change rate 86 4.3. What are the implications of the difference between satellite-based and multi-layer phenology 87 4.4. Limitations and implications for future studies 89 5. Conclusion 91 6. Appendix 92 Chapter 5. Conclusion 114 Abstract in Korean 115๋ฐ•

    Turbulent exchange of carbon dioxide in a complex urban environment : results from Long-term Eddy Covariance measurements

    Get PDF
    Within this thesis, characteristics of the turbulent exchange within the urban boundary layer, as well as long-term trends and tendencies of the carbon dioxide flux (FC) and concentration (rhoC) are presented. Prevailing transport processes, the transfer and transport efficiencies of the turbulent exchange of momentum, heat, CO2 and H2O and the importance of coherent turbulent motions within the urban boundary layer are studied by applying the quadrant analysis technique. The behavior of FC and rhoC in the urban environment is investigated on daily, seasonal, and inter-annual scales as well as in comparison to regional background concentration records of the atmospheric CO2 concentration. The dependence of the passive scalars CO2 and H2O on atmospheric stability (zeta) differs distinctly in comparison to momentum and heat. The vertical fluxes of momentum (tau) and heat (QH) are actively generating mechanically and buoyantly driven turbulence, respectively. Due to the strong coupling between tau, QH and zeta, each stability class is characterized by a distinctive turbulence regime. In contrast, the turbulent exchange of CO2 and H2O is not primarily controlled by the existence of transporting eddies, but also heavily influenced by the activity and the composition of the corresponding scalar sources (e.g. traffic, heating etc.) and thus, the heterogeneity of the local surrounding. Models represent the transfer efficiencies of momentum and heat accurately while the prediction for CO2 and H2O mostly fails. Other factors, like the interplay between the activity of sources and sinks are more important and accordingly, the transfer efficiency of CO2 can be consulted to identify times or wind sectors where the source/sink regime is altered by e.g. photosynthetic activity. The inter-comparison of the transport characteristics of heat, CO2 and H2O leads to the assumption of scalar dissimilarity. By applying the quadrant analysis framework to the long-term time series, dominant turbulent structures responsible for efficient vertical exchange, i.e. coherent structures, can be identified. The length of the time series allows to extend the analysis to the stable range, which usually rarely occurs in urban areas. The variability of local urban rhoC is investigated in comparison to regional background concentration records. While patterns on daily and seasonal scales are similar, the vicinity to the ground sources of the local measurements leads to a stronger sensitivity to changes on small temporal scales. The height above ground of the background concentration measurements and thus the larger distance from the ground sources results in a phase shift of up to three months compared to the local seasonal course of rhoC. While rhoC in the urban area is also clearly elevated by 10 ppm on average, the behavior of rhoC in the urban environment reveals good consistency with background concentration measurements in terms of seasonality and long-term trend. The calculated local linear trend for the time period between 2005 and 2014 is around 2 ppm/y, which also coincides well with the global average trend. The coupling between FC and anthropogenic activity in the urban area is apparent from considerable differences in weekday and weekend fluxes, the diurnal cycle as a result of traffic volume or the seasonality caused by additional heating activity in wintertime. The variability of FC scales with the source activity and a long-term decrease of FC around 5% is observed locally as a result of a decrease in traffic activity during the investigation period. However, variabilities on all temporal scales are clearly larger than the observed long-term tendencies. For the investigation of FC in the heterogeneous urban environment an appropriate weighting between individual wind sectors is shown to be necessary due to the unequal frequency distribution of wind directions. The application of a refined methodology for the calculation of horizontally averaged fluxes of CO2 significantly improves the representativity of the data for the investigation area and also enhances the comparability of the data to results from other studies. The length of the current dataset allows to estimate the significance of the observed long-term behavior. While up to six years are potentially needed to calculate a significant inter-annual trend of rhoC, statistics of FC still benefit from even longer data records due to the larger variability. This gives evidence, that long-term time series of urban CO2 can help to add valuable knowledge to the current understanding of the urban ecosystem and its role in the global carbon balance
    • โ€ฆ
    corecore