814 research outputs found

    Characterizing the Impacts of the Invasive Hemlock Woolly Adelgid on the Forest Structure of New England

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    Climate change is raising winter temperatures in the Northeastern United States, both expanding the range of an invasive pest, the hemlock woolly adelgid (HWA; Adelges tsugae), and threatening the survival of its host species, eastern hemlock (Tsuga canadensis). As a foundation species, hemlock trees underlie a distinct network of ecological, biogeochemical, and structural systems that will likely disappear as the HWA infestation spreads northward. Remote sensing can offer new perspectives on this regional transition, recording the progressive loss of an ecological foundation species and the transition of evergreen hemlock forest to mixed deciduous forest over the course of the infestation. Lidar remote sensing, unlike other remote sensing tools, has the potential to penetrate dense hemlock canopies and record HWA’s distinct impacts on lower canopy structure. Working with a series of lidar data from the Harvard Forest experimental site, these studies identify the unique signals of HWA impacts on vertical canopy structure and use them to predict forest condition. Methods for detecting the initial impacts of HWA are explored and a workflow for monitoring changes in forest structure at the regional scale is outlined. Finally, by applying terrestrial, airborne, and spaceborne lidar data to characterize the structural variation and dynamics of a disturbed forest ecosystem, this research illustrates the potential of lidar as a tool for forest management and ecological research

    Complexity and Dynamics of Semi-Arid Vegetation Structure, Function and Diversity Across Spatial Scales from Full Waveform Lidar

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    Semi-arid ecosystems cover approximately 40% of the earth’s terrestrial landscape and show high dynamicity in ecosystem structure and function. These ecosystems play a critical role in global carbon dynamics, productivity, and habitat quality. Semi-arid ecosystems experience a high degree of disturbance that can severely alter ecosystem services and processes. Understanding the structure-function relationships across spatial extents are critical in order to assess their demography, response to disturbance, and for conservation management. In this research, using state-of-the-art full waveform lidar (airborne and spaceborne) and field observations, I developed a framework to assess the complexity and dynamics of vegetation structure, function and diversity across spatial scales in a semi-arid ecosystem. Difficulty in differentiating low stature vegetation from bare ground is the key remote sensing challenge in semi-arid ecosystems. In this study, I developed a workflow to differentiate key plant functional types (PFTs) using both structural and biophysical variables derived from the full waveform lidar and an ensemble random forest technique. The results revealed that waveform lidar pulse width can clearly distinguish shrubs from bare ground. The models showed PFT classification accuracy of 0.81–0.86% and 0.60–0.70% at 10 m and 1 m spatial resolutions, respectively. I found that structural variables were more important than the biophysical variables to differentiate the PFTs in this study area. The study further revealed an overlap between the structural features of different PFTs (e.g. shrubs from trees). Using structural features, I derived three main functional traits (canopy height, plant area index and foliage height diversity) of shrubs and trees that describe canopy architecture and light use efficiency of the ecosystem. I evaluated the trends and patterns of functional diversity and their relationship with non-climatic abiotic factors and fire disturbance. In addition to the fine resolution airborne lidar, I used simulated large footprint spaceborne lidar representing the newly launched Global Ecosystem Dynamics Investigation system (GEDI, a lidar sensor on the International Space Station) to evaluate the potential of capturing functional diversity trends of semi-arid ecosystems at global scales. The consistency of diversity trends between the airborne lidar and GEDI confirmed GEDI’s potential to capture functional diversity. I found that the functional diversity in this ecosystem is mainly governed by the local elevation gradient, soil type, and slope. All three functional diversity indices (functional richness, functional evenness and functional divergence) showed a diversity breakpoint near elevations of 1500 m – 1700 m. Functional diversity of fire-disturbed areas revealed that the fires in our study area resulted in a more even and less divergent ecosystem state. Finally, I quantified aboveground biomass using the structural features derived from both the airborne lidar and GEDI data. Regional estimates of biomass can indicate whether an ecosystem is a net carbon sink or source as well as the ecosystem’s health (e.g. biodiversity). Further, the potential of large footprint lidar data to estimate biomass in semi-arid ecosystems are not yet fully explored due to the inherent overlapping vegetation responses in the ground signals that can be affected by the ground slope. With a correction to the slope effect, I found that large footprint lidar can explain 42% of variance of biomass with a RMSE of 351 kg/ha (16% RMSE). The model estimated 82% of the study area with less than 50% uncertainty in biomass estimates. The cultivated areas and the areas with high functional richness showed the highest uncertainties. Overall, this dissertation establishes a novel framework to assess the complexity and dynamics of vegetation structure and function of a semi-arid ecosystem from space. This work enhances our understanding of the present state of an ecosystem and provides a foundation for using full waveform lidar to understand the impact of these changes to ecosystem productivity, biodiversity and habitat quality in the coming decades. The methods and algorithms in this dissertation can be directly applied to similar ecosystems with relevant corrections for the appropriate sensor. In addition, this study provides insights to related NASA missions such as ICESat-2 and future NASA missions such as NISAR for deriving vegetation structure and dynamics related to disturbance

    닀쀑 규ëȘš LiDAR 데읎터넌 활용한 ë„ì‹œìƒíƒœêł„ ê”ŹìĄ° 및 연êČ°ì„± 평가

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    í•™ìœ„ë…ŒëŹž(ë°•ì‚Ź) -- 서욞대학ꔐ대학원 : 환êČœëŒ€í•™ì› í˜‘ë™êłŒì • ìĄ°êČœí•™, 2021.8. ì†Ąì˜ê·Œ.Integrated multiscale light detection and ranging (LiDAR) datasets are required for managing urban ecosystems because 1) LiDAR datasets can represent various spatial structures across the urban landscape and 2) the multitemporal LiDAR approach can derive the changes of urban landscape structures. This dissertation aimed to find the various spatiotemporal availabilities (i.e., from the tree-level spatial scale to the city-level regional scale with the multitemporal approach) of LiDAR or laser scanning (LS) datasets for monitoring urban ecosystems in the following three chapters. Chapter 2: Collecting tree inventory data in urban areas is important for managing green areas. Surveying using airborne laser scanning (ALS) is effective for collecting urban tree structures but less efficient regarding the economic costs and its operation. Terrestrial laser scanning (TLS), and mobile laser scanning (MLS) datasets could have the potential in complementing those of ALS in the respect to efficiency. However, to the best of my knowledge, there were limited studies for seeking the similarities and variations among the canopy metrics derived from various LiDAR platforms. In Chapter 2, I compared structural canopy metrics among ALS, TLS, and MLS datasets in the urban parks. The purpose of Chapter 2 was to test whether the estimates of tree metrics differed depending on single or clustered trees and to test whether the errors in LiDAR-derived metrics were related to the tree structures. Small, urban parks were selected for surveying trees using the three LiDAR platforms. The ALS datasets were acquired on 14 May, 2017. The TLS and MLS datasets were acquired from 10–11 May, 2017, and 21–25 April, 2020, respectively. The tree point clouds were classified into single and clustered trees. The structural metrics were compared in each pair (i.e., ALS and TLS, ALS and MLS, and TLS and MLS pairs). The heights related metrics (e.g., percentile heights and the distribution of the heights values), the complexity metric (e.g., the Rumple index) and area were calculated for comparisons. The root mean square error (RMSE), bias, and the Pearson’s correlation coefficient (r) were calculated to evaluate the difference in each metric among the LiDAR platforms. The results showed that ZMAX, max and mean CHM, and area showed good consistencies (RMSE% 0.900). Especially, the biases of CHM-derived metrics did not present significant differences (p > 0.05) regardless of single or clustered trees. Moreover, the biases from the comparisons in each pair showed linear relations with the tree heights and vertical canopy complexity (i.e., Pearson’s correlation coefficient showed significant; r >0.29, p < 0.05). My results could be references when combining multiple LiDAR systems to estimate the canopy structures of urban park areas. Chapter 3: Understanding forest dynamics is important for assessing the health of urban forests, which experience various disturbances, both natural (e.g., treefall events) and artificial (e.g., making space for agricultural fields). Therefore, quantifying three-dimensional (3D) changes in canopies is a helpful way to manage and understand urban forests better. Multitemporal ALS datasets enable me to quantify the vertical and lateral growth of trees across a landscape scale. The goal of Chapter 3 is to assess the annual changes in the 3-D structures of canopies and forest gaps in an urban forest using annual airborne LiDAR datasets for 2012–2015. The canopies were classified as high canopies and low canopies by a 5 m height threshold. Then, I generated pixel- and plot-level canopy height models and conducted change detection annually. The vertical growth rates and leaf area index showed consistent values year by year in both canopies, while the spatial distributions of the canopy and leaf area profile (e.g., leaf area density) showed inconsistent changes each year in both canopies. In total, high canopies expanded their foliage from 12 m height, while forest gap edge canopies (including low canopies) expanded their canopies from 5 m height. Annual change detection with LiDAR datasets might inform about both steady growth rates and different characteristics in the changes of vertical canopy structures for both high and low canopies in urban forests. Chapter 4: Although many studies have considered urban structure when investigating urban ecological networks, few have considered the 3D structure of buildings as well as urban green spaces. In Chapter 4, I examined an urban ecological network using the 3D structure of both green spaces and buildings. Using breeding-season bird species observations and ALS data collected, I assessed the influence of 3D structural variables on species diversity. I used correlation analyses to determine if vertical distribution, volume, area, and height of both buildings and vegetation were related to bird species diversity. Then I conducted circuit theory-based current flow betweenness centrality (CFBC) analysis using the LiDAR-derived structural variables. I found that the volumes of buildings and 8–10 m vegetation heights were both highly correlated with species richness per unit area. There were significant differences between 2D and 3D connectivity analysis using LiDAR-derived variables among urban forest patches, boulevards, and apartment complexes. Within urban forest patches and parks, 3D CFBC represented canopy structural characteristics well, by showing high variance in spatial distributions. The 3D CFBC results indicated that adjacent high-rise buildings, dense apartment complexes, and densely urbanized areas were isolated, as characterized by low centrality values, but that vegetation planted in open spaces between buildings could improve connectivity by linking isolated areas to core areas. My research highlights the importance of considering 3D structure in planning and managing urban ecological connectivity. In this dissertation, the availability of integrated multiscale LiDAR datasets was found via three standalone studies. It was revealed that 3D information could enhance the quality of urban landscape monitoring and ecological connectivity analysis by elaborately explaining spatial structures. However, the spatiotemporal scales of each standalone study were limited to the city scale and to five years. The recently launched Global Ecosystem Dynamics Investigation (GEDI) would help to solve these limitations. Furthermore, the GEDI dataset could help researchers understand the relationship between ecosystem structures and their functions.ëłž í•™ìœ„ë…ŒëŹžì€ 닀양한 ì‹œêł”ê°„ 슀쌀음에서 ë„ì‹œìƒíƒœêł„ ëȘšë‹ˆí„°ë§ì„ 위한 LiDAR 데읎터의 í™œìš©êłŒ 생태적 ì˜ëŻž 도출에 ꎀ한 낎용을 닀룏닀. LiDAR란 Light Detection and Ranging의 ì•œì–ŽëĄœ, LiDAR 섌서에서 ë°œì‚Źëœ 레읎저가 대상에 도달한 ë’€ ë°˜ì‚Źë˜ì–Ž 돌아였는 레읎저의 섞Ʞ와 시간을 êł„ì‚°í•˜ì—Ź 대상의 위ìč˜ ì •ëłŽë„Œ 3찚원 점ꔰ ë°ìŽí„°ëĄœ ëł€í™˜í•ŽìŁŒëŠ” 늄동형 원êČ©íƒì‚Ź ë„ê”ŹìŽë‹€. LiDAR 원êČ©íƒì‚Ź ë„ê”Źì˜ ë“±ìž„ìœŒëĄœ ìžì—°êłŒ 도시의 3찚원 êł”ê°„ì •ëłŽì˜ 췚득읎 Ʞ늄핎짐에 따띌, 서식지의 3찚원 êł”ê°„ì •ëłŽì™€ ìƒëŹŒ ìą… ì‚ŹìŽì˜ êŽ€êł„ 도출, ì‹œêł„ì—Ž LiDAR 데읎터넌 활용한 ë…č지 ëȘšë‹ˆí„°ë§ ì—°ê”Ź 등읎 ìŽë€„ì§€êł  있닀. 또한 í•­êł” LiDAR(ALS), 지상 LiDAR(TLS), 읎동형 LiDAR(MLS) 등 닀양한 LiDAR 시슀템의 ê°œë°œëĄœ ì—°ê”Ź ëȘ©ì ì— 알맞은 ì‹œêł”ê°„ 핎상도의 3찚원 êł”ê°„ì •ëłŽë„Œ 췚득할 수 있êȌ 되었닀. ëłž í•™ìœ„ë…ŒëŹžì—ì„œëŠ” 도시ë…č지넌 ëŒ€ìƒìœŒëĄœ LiDAR 원êČ©íƒì‚Ź ë„ê”Źì˜ 닀양한 ì‹œêł”ê°„ 슀쌀음 적용 ìžĄë©Žì—ì„œ, Chapter 2 í•­êł”, 지상, 읎동형 LiDAR 시슀템 ì‚ŹìŽ 수ëȘ©ê”ŹìĄ°êŽ€ë š ëł€ìˆ˜ë“€ì˜ 음ìč˜ì„± 평가, Chapter 3 ì‹œêł„ì—Ž 분석을 톔한 도시ë…č지 동태 ëȘšë‹ˆí„°ë§, Chapter 4 도시의 생태적 연êČ°ì„± 분석을 진행하였닀. Chapter 2: 도시의 수ëȘ©ì •ëłŽë„Œ 췚득하는 êČƒì€ 도시ë…č지 êŽ€ëŠŹì— 있얎 필수적읎닀. LiDAR Ʞ술의 발달로 도시수ëȘ©ì˜ 3찚원 ì •ëłŽë„Œ 췚득할 수 있êȌ 되었윌며, 읎넌 톔핎 수ëȘ©ë†’읎와 수ëȘ©ê”ŹìĄ°, 지상 바읎였맀슀 등을 높은 ì •í™•ë„ëĄœ 산출할 수 있êȌ 되었닀. í•­êł” LiDAR는 넓은 ëČ”ìœ„ì˜ êł”ê°„ì •ëłŽë„Œ 높은 ì •í™•ë„ëĄœ ìžĄì •í•˜ëŠ” íŠč성을 지녀 산늌 ëȘšë‹ˆí„°ë§ 분알에서 활발히 í™œìš©ë˜êł  있닀. 하지만 í•­êł” LiDAR 데읎터의 췚득은 í•­êł”êž° 욎용ëč„, 임ëč„ꎀ렚 막대한 ëč„용읎 ë°œìƒí•˜êł  욎용에 있얎 ì „ëŹžì„±ì„ ìš”ê”Źí•˜ë©° 대상의 점ꔰ밀도가 ìƒëŒ€ì ìœŒëĄœ 낟닀는 닚점을 지닌닀. 반멎 지상 LiDAR와 읎동형 LiDAR는 욎용하Ʞ íŽžëŠŹí•˜êł  높은 점ꔰ밀도넌 출렄한닀는 점에서 í•­êł” LiDAR의 닚점을 ê·č볔할 수 있닀. 읎ìČ˜ëŸŒ 닀양한 LiDAR 시슀템의 ë“±ìž„êłŒ 읎넌 활용한 ìƒíƒœêł„ ëȘšë‹ˆí„°ë§ ì—°ê”Ź 시도가 슝가하멎서 LiDAR 시슀템간 횚윚적읞 ìšŽìš©êłŒ 데읎터의 ëłŽì™„ ë°©ëČ•ë“€ìŽ ìš”ê”Źë˜êł  있닀. 하지만 í˜„ìžŹêčŒì§€ ALS, TLS, MLS의 3개의 시슀템을 톔핎 췚득된 수ëȘ© ì •ëłŽë„Œ ì„œëĄœ ëč„ê”í•˜êł , ì„œëĄœ 대ìČŽê°€ëŠ„í•œ 수ëȘ©ì •ëłŽë„Œ 도출한 ì—°ê”ŹëŠ” 많읎 진행된 바 없닀. 따띌서 ëłž í•™ìœ„ë…ŒëŹžì˜ Chapter 2에서는 ALS, TLS, MLS 톔핎 췚득된 도시의 수ëȘ©ì •ëłŽë„Œ ì„œëĄœ ëč„ê”í•˜ì—Ź 음ìč˜ì„±ì„ í‰ê°€í•˜êł , ì–Žë– í•œ 수ëȘ©ê”ŹìĄ°êŽ€ë š 지표가 ì„ž LiDAR 시슀템 ì‚ŹìŽì—ì„œ 대ìČŽê°€ëŠ„í•œì§€ ë‹€ëŁšêł  있닀. ì„žë¶€ì ìœŒëĄœ Chapter 2는 수ëȘ©ê”ŹìĄ°êŽ€ë š 지표가 당ëȘ©ì°šì›êłŒ ꔰ집찚원, 수ëȘ©ê”ŹìĄ°ì— 따띌 ALS, TLS, MLS 시슀템에서 찚읎가 발생하는지에 대한 낎용을 ë‹Žêł  있닀. ìČœì•ˆì‹œ ë„ì‹œêł”ì› 9개소에서 ALS 데읎터는 2017년 5월 14음, TLS 데읎터는 2017년 5월 10ìŒêłŒ 11음, MLS 데읎터는 2020년 4월 21에서 25음 췚득되었닀. 췚득된 데읎터셋은 수ꎀ의 êČčìčš ì—Źë¶€ì— 따띌 당ëȘ©êłŒ ê”°ì§‘ìœŒëĄœ 분넘되었윌며, 3개의 페얎(ALS-TLS, MLS-TLS, ALS-MLS)로 수ꎀ의 퍌섌타음 높읎, ìˆ˜êŽ€ëł”ìžĄì„±, 멎적 등의 수ëȘ©ê”ŹìĄ°êŽ€ë š ëł€ìˆ˜ë“€ì„ 1:1 ëč„ꔐ하였닀. í•­êł” LiDAR 데읎터넌 톔핎 도출된 수ëȘ©ê”ŹìĄ°êŽ€ë š ëł€ìˆ˜ë“€ì„ ì°žìĄ°ëĄœ í•˜ì—Ź í‰ê· ì œêł±ê·Œì˜€ì°š(RMSE), 펞햄(bias), 플얎슚 ìƒêŽ€êł„ìˆ˜(r) 등을 êł„ì‚°í•˜êł  ì„ž LiDAR 시슀템 ì‚ŹìŽì˜ 음ìč˜ì„±ì„ 평가하였닀. 평가 êČ°êłŒ ZMAX, CHMꎀ렚 수ꎀ높읎 ꎀ렚 ëł€ìˆ˜ë“€, ê·žëŠŹêł  수ꎀ멎적읎 높은 음ìč˜ì„±ì„ ëłŽì˜€ë‹€(RMSE% 0.900). íŠč히 CHM을 톔핎 도출된 수ꎀ높읎 ꎀ렚 ëł€ìˆ˜ë“€ì€ 당ëȘ©êłŒ ꔰ집에서 섞개의 LiDAR 시슀템간 í†”êł„ì ìž 찚읎넌 ëłŽìŽì§€ 않았닀(p > 0.05). 반멎 퍌섌타음 수ꎀ높읎와 평균 수ꎀ높읎 등은 맀우 ë‚źì€ 음ìč˜ì„±ì„ 나타냈윌며, ì„ž 페얎에서 도출된 펞햄은 ìˆ˜êł , ìˆ˜êŽ€ëł”ìžĄì„±êłŒ 앜한 ì„ í˜•êŽ€êł„ë„Œ 나타냈닀(r >, p < 0.05). Chapter 3: 수ꎀ동태는 ìˆČ의 걎강성을 반영한닀. íŠč히, 자연적·읞위적읞 ꔐ란에 의핎 발생한 ìˆČ틈은 ìˆČ 낎부에 ëč›ì˜ íˆŹêłŒìœš, 옚도, 슔도 등에 영햄을 ëŒìł ìŁŒëł€ 환êČœì˜ ëł€í™”ë„Œ 알Ʞ한닀. 따띌서 ìˆČ틈을 íƒì§€í•˜êł  ëȘšë‹ˆí„°ë§í•˜ëŠ” êČƒì€ ìˆČ의 동태넌 읎핎하는데 있얎 맀우 쀑요하닀. í•­êł” LiDAR 섌서넌 활용할 êČœìš° 위성영상읎나 í•­êł”ì‚Źì§„ 등 2찚원 ë°ìŽí„°ëĄœ 탐지하Ʞ 얎렀욎 ìˆČ틈 또는 ê°œë°©êł”ê°„ì˜ 탐지와 수ꎀ의 3찚원 형상의 췚득읎 가늄하닀. Chapter 3에서는 2012년도부터 2015년도 4개년의 í•­êł” LiDARë„Œ í™œìš©í•˜ì—Ź 자연형 ë„ì‹œêł”ì›(뎉서산)의 ìˆ˜êŽ€êłŒ ìˆČ틈의 수평적 수직적 ëł€í™”ì–‘ìƒì„ 추정하였닀. 수ꎀ은 높읎 5më„Œ êž°ì€€ìœŒëĄœ 상잔부와 하잔부 ìˆ˜êŽ€ìœŒëĄœ 분넘되었윌며, 수ꎀ높읎ëȘšëž(canopy height model, CHM)을 ìƒì„±í•˜ì—Ź ì—°ê°„ëł€í™”ë„Œ 탐지하였닀. ì—°ê”ŹêČ°êłŒ 상잔부 및 하잔부 수ꎀ의 ìˆ˜ì§ìƒìž„ëŸ‰êłŒ 엜멎적지수는 음정한 연간 ëł€í™”ì–‘ìƒì„ ëłŽìž 반멎, 수평적 ëł€í™”ì™€ 엜멎적밀도는 불규ìč™ì ìž 연간 ëł€í™”ì–‘ìƒì„ ëłŽì˜€ë‹€. ì „ë°˜ì ìœŒëĄœ 상잔부 수ꎀ은 높읎 12m에서 ìžĄë°©í–„ 생임을 하는 êČƒìœŒëĄœ ë‚˜íƒ€ë‚ŹìœŒë©°, 하잔부 수ꎀ 쀑 ìˆČ틈에서는 높읎 5m에서 ìžĄë°©í–„ 생임읎 활발하êȌ ë‚˜íƒ€ë‚Źë‹€. LiDAR 데읎터의 연간 변화 탐지넌 톔핎 ìžì—°ì ìœŒëĄœ 형성된 ìˆČ틈의 êČœìš° ìƒìž„êłŒ ꔐ란 ìžĄë©Žì—ì„œ 맀우 활발한 동태가 ë°œìƒí•˜êł  있윌며, ìžìœ„ì ìœŒëĄœ 형성된 ê°œë°©êł”ê°„ì˜ êČœìš° 수ꎀ의 동태가 닀소 ìčšìČŽëšì„ 도출하였닀. Chapter 4는 도시 낮 ê±ŽëŹŒêłŒ ë…č지의 3찚원 ê”ŹìĄ°ë„Œ ìž…ë „ìžëŁŒëĄœ í™œìš©í•˜ì—Ź 도시의 생태적 연êČ°ì„±ì„ 평가하는 ì—°ê”Źë„Œ 닀룏닀. 도시 낮 생태적 연êČ°ì„± ë„ì¶œêłŒ ꎀ렚한 ì—°ê”ŹëŠ” 도시와 ë…č지의 형태 등을 ìŁŒìš” ëł€ìˆ˜ëĄœ í•˜ì—Ź 진행읎 ë˜êł  있닀. ê·žëŸŹë‚˜ 3찚원적읞 íŠč성읞 도시 ê±ŽëŹŒì˜ 부플, 수ëȘ©ì˜ 수직적읞 ê”ŹìĄ° 등을 êł ë €í•œ 연êČ°ì„± 분석은 많읎 진행된 바 없닀. ì—°ê”Ź 대상지는 ìČœì•ˆì‹œ 시ìČ­ì„ ì€‘ì‹ŹìœŒëĄœí•œ 4 km × 4 km ì§€ì—­ìœŒëĄœ, 2015년에 췚득된 í•­êł” LiDAR와 같은 핮 췚득된 ìĄ°ë„˜ ìą… ìĄ°ì‚Ź 데읎터넌 í™œìš©í•˜ì—Ź 1)도시 낮 ê±ŽëŹŒêłŒ ë…č지의 3찚원 ê”ŹìĄ°ì™€ ìĄ°ë„˜ ìą… 닀양성 ì‚ŹìŽ êŽ€êł„ë„Œ ì‚Ží”Œêł , 2)ìĄ°ë„˜ ìą… ë‹€ì–‘ì„±êłŒ ìƒêŽ€êŽ€êł„ë„Œ 가지는 3찚원 ê”ŹìĄ°ëł€ìˆ˜ë„Œ í™œìš©í•˜ì—Ź 전넘흐늄Ʞ반 ë§€ê°œì€‘ì‹Źì„± 연êČ°ì„± 분석(CFBC)을 진행하였닀. ì—°ê”ŹêČ°êłŒ ê±Žì¶•ëŹŒì˜ 부플와 수ëȘ©ë†’읎 8-10m의 ë…č지 부플ëč„ê°€ 멎적ë‹č ìĄ°ë„˜ ìą… 풍부도와 슀플얎만 ìˆœìœ„ìƒêŽ€êŽ€êł„ì—ì„œ 높은 ìƒêŽ€êŽ€êł„(ρ> 0.6)ë„Œ 나타냈닀. 연êČ°ì„± 분석의 êČ°êłŒëŠ” ìž…ë „ëł€ìˆ˜ì˜ êł”ê°„ì°šì›(2D 및 3D)에 따띌 닀넎êȌ ë‚˜íƒ€ë‚Źë‹€. íŠč히 도시ìˆČ, 대로변, 아파튞닚지낎 ë…č지 등에서 2D êž°ë°˜ CFBC와 3Dêž°ë°˜ CFBC는 í†”êł„ì ìœŒëĄœ ìœ ì˜ëŻží•œ 찚읎넌 ëłŽì˜€ë‹€. 또한 도시ë…č지의 3D êž°ë°˜ CFBC의 êČœìš° 같은 ë…č지 멎적임에도 수ꎀ의 ê”ŹìĄ°ì ìž íŠč성에 따띌 높은 찚읎가 나타낚을 확읞하였닀. 3D CFBC 분석êČ°êłŒë„Œ 톔핎 êł ìž” ê±ŽëŹŒ ìŁŒëł€ë¶€, êł ë°€ë„ 아파튞닚지, êł ë°€ 시가화지역 등읎 ë‚źì€ ì€‘ì‹Źì„±ì„ ëłŽì—Ź êł ëŠœì§€ì—­ìœŒëĄœ ë‚˜íƒ€ë‚ŹìœŒë©°, ê±ŽëŹŒ ì‚ŹìŽ êł”ì§€ 낮 식생은 연êČ°ì„±ìŽ êł ëŠœëœ ì§€ì—­êłŒ í•”ì‹Źì§€ì—­ì„ 연êȰ하는 Ʞ늄을 나타냈닀. 읎 í•™ìœ„ë…ŒëŹžì€ ì„œëĄœ 닀넞 LiDAR 시슀템을 í™œìš©í•˜ì—Ź 당ëȘ©, êČœêŽ€ 지역닚위 등 닀양한 êł”ê°„ 슀쌀음에서의 도시êČœêŽ€ê”ŹìĄ° 분석, 도시ë…čì§€ê”ŹìĄ°ì™€ 토지읎용 등에 ë”°ë„ž 시간적 ëł€í™”ì–‘ìƒ, 도시êČœêŽ€ê”ŹìĄ°ê°€ 가지는 생태적 ì˜ëŻž ë“±êłŒ ꎀ렚된 낎용을 ë‹€ëŁšêł  있닀. 햄후 Global Ecosystem Dynamics Investigation(GEDI) ëŻžì…˜ì˜ 데읎터넌 í™œìš©í•˜ì—Ź ëłž í•™ìœ„ë…ŒëŹžì—ì„œ 닀룚는 지역규ëȘšì˜ ì—°ê”Źë„Œ ꔭ가닚위, 대넙닚위 ë“±ìœŒëĄœ 확임할 수 있을 êČƒìŽë©° 읎넌 톔핎 ë„ì‹œìƒíƒœêł„ ê”ŹìĄ°ì™€ ê·ž Ʞ늄 ì‚Źì˜ êŽ€êł„ë„Œ 읎핎하는데 도움을 쀄 수 있을 êČƒìŽë‹€.Chapter 1. Introduction 1 1. Background 1 1.1. Urbanization and the importance of urban green spaces 1 1.2. Urban landscape and Light detection and ranging application 1 2. Purpose 6 Chapter 2. Comparing tree structures derived among multiple LiDAR systems in urban parks 10 1. Introduction 10 2. Methods and materials 12 2.1. Study site and tree classification 12 2.2. LiDAR survey and processing 14 2.3. Deriving the structural variables of the parks 17 2.4. Assessing the accuracy of the LiDAR-derived indices 18 3. Results 19 3.1. Comparing height metrics among the three LiDAR systems 19 3.2. Comparing CHM-derived canopy height metrics from each LiDAR systems 22 3.3. Comparing the area and the Rumple index determined using the LiDAR systems 23 4. Discussion 25 4.1. LiDAR configurations and data acquisition time intervals 25 4.2. Uncertainty of the structural indices derived from the three LiDAR systems 28 Chapter 3. Urban forest growth and gap dynamics detected by yearly repeated airborne LiDAR 31 1. Introduction 31 2. Methods and Materials 33 2.1. Field survey 33 2.2. Canopy opening detection 34 2.3. Airborne LiDAR dataset acquisition and registration 35 2.4. Generation of height models and change detection 36 2.5. Gap detection and classification 38 2.6. Estimating changes of vertical canopy distribution and canopy complexity 38 3. Results 39 3.1. Pixel and hexagon height model-based change detection 39 3.2. Continuous one-year vertical growth area 41 3.3. Open canopy change detection 42 3.4. Changes in vertical canopy structures in High Canopy and Open Canopy 43 4. Discussion 45 4.1. What are the differences between the canopy structural changes derived from annual change detections and three-year interval change detection? 45 4.2. What are the characteristics of the structural changes according to the different canopy classes (e.g., high canopies and low canopies) in the urban forest? 46 Chapter 4. LiDAR-derived three-dimensional ecological connectivity mapping 49 1. Introduction 49 2. Materials and Methods 51 2.1. Study area and avian species observation 52 2.2. Airborne LiDAR acquisition, preprocessing and classification and deriving structural variables 53 2.3. Correlation analysis and selection of structural variables 55 2.4. 2D and 3D ecological networks 55 3. Results 56 3.1. Avian species survey 56 3.2. Correlation analyses and variable selection 56 3.3. Connectivity analysis results 58 3.4. Correlation between connectivity results with bird species diversity 59 3.5. Differences between 2D- and 3D-based CFBCs 60 4. Discussion 61 4.1. Vegetation and building structures and bird species diversity 61 4.2. 3D-based connectivity results 62 4.3. Differences between 2D and 3D network analyses 64 4.3.1. Forest and artificial green area 65 4.3.2. Roads and residential areas 66 Appendix 67 Chapter 5. Conclusion 70 1. Combination with multiple LiDAR data for surveying structures of urban green spaces 70 2. Multi-temporal urban forest gap monitoring 71 3. Ecological connectivity analysis using LiDAR 71 4. LiDAR application to Urban ecosystem monitoring 72 5. Expanding spatiotemporal scale and further works 73 Acknowledgments 75 Reference 76 Abstract in Korean 85박

    Advancing savanna structural characterization at multiple scales for enhanced ecological insights

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    The Burning Bush: Linking LiDAR-derived Shrub Architecture to Flammability

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    Light detection and ranging (LiDAR) and terrestrial laser scanning (TLS) sensors are powerful tools for characterizing vegetation structure and for constructing three-dimensional (3D) models of trees, also known as quantitative structural models (QSM). 3D models and structural traits derived from them provide valuable information for biodiversity conservation, forest management, and fire behavior modeling. However, vegetation studies and 3D modeling methodologies often only focus on the forest canopy, with little attention given to understory vegetation. In particular, 3D structural information of shrubs is limited or not included in fire behavior models. Yet, understory vegetation is an important component of forested ecosystems, and has an essential role in determining fire behavior. In this dissertation, I explored the use of TLS data and quantitative structure models to model shrub architecture in three related studies. In the first study, I present a semi-automated methodology for reconstructing architecturally different shrubs from TLS LiDAR. By investigating shrubs with different architectures and point cloud densities, I showed that occlusion, shrub complexity, and shape greatly affect the accuracy of shrub models. In my second study, I assessed the 3D architectural drivers of understory flammability by evaluating the use of architectural metrics derived from the TLS point cloud and 3D reconstructions of the shrubs. I focused on eight species common in the understory of the fire-prone longleaf pine forest ecosystem of the state of Florida, USA. I found a general tendency for each species to be associated with a unique combination of flammability and architectural traits. Novel shrub architectural traits were found to be complementary to the direct use of TLS data and improved flammability predictions. The inherent complexity of shrub architecture and uncertainty in the TLS point cloud make scaling up from an individual shrub to a plot level a challenging task. Therefore, in my third study, I explored the effects of lidar uncertainty on vegetation parameter prediction accuracy. I developed a practical workflow to create synthetic forest stands with varying densities, which were subsequently scanned with simulated terrestrial lidar. This provided data sets quantitatively similar to those created by real-world LiDAR measurements, but with the advantage of exact knowledge of the forest plot parameters, The results showed that the lidar scan location had a large effect on prediction accuracy. Furthermore, occlusion is strongly related to the sampling density and plot complexity. The results of this study illustrate the potential of non-destructive lidar approaches for quantifying shrub architectural traits. TLS, empirical quantitative structural models, and synthetic models provide valuable insights into shrub structure and fire behavior

    Assessing the utility of geospatial technologies to investigate environmental change within lake systems

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    Over 50% of the world's population live within 3. km of rivers and lakes highlighting the on-going importance of freshwater resources to human health and societal well-being. Whilst covering c. 3.5% of the Earth's non-glaciated land mass, trends in the environmental quality of the world's standing waters (natural lakes and reservoirs) are poorly understood, at least in comparison with rivers, and so evaluation of their current condition and sensitivity to change are global priorities. Here it is argued that a geospatial approach harnessing existing global datasets, along with new generation remote sensing products, offers the basis to characterise trajectories of change in lake properties e.g., water quality, physical structure, hydrological regime and ecological behaviour. This approach furthermore provides the evidence base to understand the relative importance of climatic forcing and/or changing catchment processes, e.g. land cover and soil moisture data, which coupled with climate data provide the basis to model regional water balance and runoff estimates over time. Using examples derived primarily from the Danube Basin but also other parts of the World, we demonstrate the power of the approach and its utility to assess the sensitivity of lake systems to environmental change, and hence better manage these key resources in the future

    Assessing wood properties in standing timber with laser scanning

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    Managed forests play crucial roles in ongoing climatic and environmental changes. Among other things, wood is capable of sinking and storing carbon in both standing timber and wood products. To promote these positive effects, more precise planning is required that will ensure sustainable forest management and maximal deposition of harvested wood for long-term applications. Information on wood properties plays a key role; i.e. the wood properties can impact the carbon stocks in forests and the suitability of wood for structural timber. With respect to the theoretical background of wood formation, stem, crown, and branching constitute potential inputs (i.e. wood quality indicators) to allometric wood property, tree biomass, and wood quality models. Due to the complex nature of wood formation, measurements of wood quality indicators that could predict wood properties along the relevant directions of variation have previously been elusive in forest inventories. However, developments in laser scanning from aerial and terrestrial platforms support more complex mapping and modeling regimes based on dense three-dimensional point clouds. The aim here was to determine how wood properties could be estimated in remote-sensing-aided forest inventories. For this purpose, methods for characterizing select wood quality indicators in standing timber, using airborne and terrestrial laser scanning (ALS and TLS, respectively) were developed and evaluated in managed boreal Scots pine (Pinus sylvestris L.) forests. Firstly, the accuracies of wood quality indicators resolved from TLS point clouds were assessed. Secondly, the results were compared with x-ray tomographic references from sawmills. Thirdly, the accuracies of tree-specific crown features delineated from the ALS data in predictive modeling of the wood quality indicators were evaluated. The results showed that the quality and density of point clouds significantly impacted the accuracies of the extracted wood quality indicators. In the assessment of wood properties, TLS should be considered as a tool for retrieving as dense stem and branching data as possible from carefully selected sample trees. Accurately retrieved morphological data could be applied to allometric wood property models. The models should use tree traits predictable with aerial remote sensing (e.g. tree height, crown dimensions) to enable extrapolations. As an outlook, terrestrial and aerial remote sensing can play an important role in filling in the knowledge gaps regarding the behavior of wood properties over different spatial and temporal extents. Further interdisciplinary cooperation will be needed to fully facilitate the use of remote sensing and spatially transferable wood property models that could become useful in tackling the challenges associated with changing climate, silviculture, and demand for wood.Hoidetuilla metsillÀ on useita tÀrkeitÀ rooleja muuttuvassa ilmastossa ja ympÀristössÀ. Puu sitoo ja varastoi hiiltÀ niin kasvaessaan, kuin pitkÀikÀisiksi puutuotteiksi jalostettuna. NÀiden vaikutusten huomioiminen metsÀnhoidossa vaatii tarkkaa suunnittelua, jolla varmistetaan metsÀnhoidon ja puunkÀytön kestÀvyys. Tieto puuaineen ominaisuuksista on keskeisessÀ osassa, sillÀ ne vaikuttavat hiilivarastojen suuruuteen metsissÀ, sekÀ puun kÀytettÀvyyteen pitkÀikÀisenÀ rakennesahatavarana. Puunmuodostuksen teoreettisen taustan mukaisesti, runko, latvus ja oksarakenne ovat potentiaalisia selittÀviÀ muuttujia (eli puun laatuindikaattoreita), kun mallinnetaan puuaineen ominaisuuksia, puubiomassaa ja puun laatua. Puunmuodostuksen monimutkaisuudesta ja moniulotteisesta vaihtelusta johtuen, tarvittavien laatuidikaattorien mittaaminen osana metsÀvarojen inventointia ja riittÀvÀllÀ yksityiskohtaisuudella on ollut aiemmin mahdotonta. Monialustaisen laserkeilauksen kehittyminen kuitenkin tukee aiempaa monipuolisempien kartoitus- ja mallinnusjÀrjestelmien rakentamista, jotka perustuvat tiheisiin kolmiulotteisiin pistepilviin. TÀmÀn työn tavoitteena oli mÀÀritellÀ, kuinka puuaineen ominaisuuksia voidaan arvioida kaukokartoitusta hyödyntÀvÀssÀ metsÀvarojen inventoinnissa. TÀtÀ tarkoitusta varten kehitettiin menetelmiÀ puun laatuindikaattorien mittaamiseksi hoidetuissa mÀnniköissÀ (Pinus sylvestris L.) lento- ja maastolaserkeilauksen avulla, ja arvioitiin niiden toimivuutta. Ensin arvioitiin laatuindikaattorien mittatarkkuus pistepilvissÀ. Toiseksi verrattiin pistepilvimittauksia röntgentomografiamittauksiin teollisilla sahoilla. Kolmanneksi arvioitiin lentolaserkeilauksella tuotettujen latvuspiirteiden tarkkuutta laatuindikaattorien ennustamisessa. Tuloksien perusteella pistepilvien laatu ja pistetiheys vaikuttivat merkittÀvÀsti mitattujen laatuindikaattorien tarkkuuteen. Puuaineen ominaisuuksien arvioimisessa, maastolaserkeilausta tulisi kÀyttÀÀ työkaluna mahdollisimman yksityiskohtaisten runko- ja oksikkuustietojen kerÀÀmiseen tarkkaan valikoiduista nÀytepuista. Tarkasti mitatut laatuindikaattorit voivat selittÀÀ puuaineen ominaisuuksia mallinnuksessa. KÀytettyjen mallien tulisi perustua laatuindikaattoreille, jotka voidaan ennustaa lentolaserkeilausaineistosta (esim. puun pituus ja latvuksen mittasuhteet), jotta ennusteet ovat yleistettÀvissÀ laajoille alueille. Tulevaisuudessa, maasta ja ilmasta tehtÀvÀllÀ kaukokartoituksella voi olla tÀrkeÀ rooli puuaineen ominaisuuksien aikaan ja paikkaan sidotun vaihtelun tutkimuksessa. LisÀÀ poikkitieteellistÀ työtÀ tarvitaan, jotta kaukokartoitusta ja puuaineen ominaisuuksia ennustavia spatiaalisia malleja voidaan tÀysimittaisesti hyödyntÀÀ kiihtyvÀn ilmastonmuutoksen, muuttuvan metsÀnhoidon ja lisÀÀntyvÀn puunkÀytön tuomien haasteiden kohtaamisessa

    Spaceborne Lidar in the Study of Marine Systems

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    Satellite passive ocean color instruments have provided an unbroken ~20-year record of global ocean plankton properties, but this measurement approach has inherent limitations in terms of spatial-temporal sampling and ability to resolve vertical structure within the water column. These limitations can be addressed by coupling ocean color data with measurements from a spaceborne lidar. Airborne lidars have been used for decades to study ocean subsurface properties, but recent breakthroughs have now demonstrated that plankton properties can be measured with a satellite lidar. The satellite lidar era in oceanography has arrived. Here we present a review of the lidar technique, its applications in marine systems, a prospective on what can be accomplished in the near future with an ocean- and atmosphere-optimized satellite lidar, and a vision for a multi-platform virtual constellation of observational assets enabling a 3-dimensional reconstruction of global ocean ecosystems

    A backpack-mounted omnidirectional camera with off-the-shelf navigation sensors for mobile terrestrial mapping: Development and forest application

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    The use of Personal Mobile Terrestrial System (PMTS) has increased considerably for mobile mapping applications because these systems offer dynamic data acquisition with ground perspective in places where the use of wheeled platforms is unfeasible, such as forests and indoor buildings. PMTS has become more popular with emerging technologies, such as miniaturized navigation sensors and off-the-shelf omnidirectional cameras, which enable low-cost mobile mapping approaches. However, most of these sensors have not been developed for high-accuracy metric purposes and therefore require rigorous methods of data acquisition and data processing to obtain satisfactory results for some mapping applications. To contribute to the development of light, low-cost PMTS and potential applications of these off-the-shelf sensors for forest mapping, this paper presents a low-cost PMTS approach comprising an omnidirectional camera with off-the-shelf navigation systems and its evaluation in a forest environment. Experimental assessments showed that the integrated sensor orientation approach using navigation data as the initial information can increase the trajectory accuracy, especially in covered areas. The point cloud generated with the PMTS data had accuracy consistent with the Ground Sample Distance (GSD) range of omnidirectional images (3.5–7 cm). These results are consistent with those obtained for other PMTS approaches. View Full-Text Keywords: personal mobile terrestrial system; omnidirectional cameras; low-cost sensors; forest mapping; PMTS data quality </div
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