435 research outputs found

    Individualization of Pinus radiata Canopy from 3D UAV Dense Point Clouds Using Color Vegetation Indices

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    The location of trees and the individualization of their canopies are important parameters to estimate diameter, height, and biomass, among other variables. The very high spatial resolution of UAV imagery supports these processes. A dense 3D point cloud is generated from RGB UAV images, which is used to obtain a digital elevation model (DEM). From this DEM, a canopy height model (CHM) is derived for individual tree identification. Although the results are satisfactory, the quality of this detection is reduced if the working area has a high density of vegetation. The objective of this study was to evaluate the use of color vegetation indices (CVI) in canopy individualization processes of Pinus radiata. UAV flights were carried out, and a 3D dense point cloud and an orthomosaic were obtained. Then, a CVI was applied to 3D point cloud to differentiate between vegetation and nonvegetation classes to obtain a DEM and a CHM. Subsequently, an automatic crown identification procedure was applied to the CHM. The results were evaluated by contrasting them with results of manual individual tree identification on the UAV orthomosaic and those obtained by applying a progressive triangulated irregular network to the 3D point cloud. The results obtained indicate that the color information of 3D point clouds is an alternative to support individualizing trees under conditions of high-density vegetation

    Assessing biodiversity using forest structure indicators based on airborne laser scanning data

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    The role of forests in biodiversity assessment and planning is substantial as these ecosystems support approximately 80% of the worldโ€™s terrestrial biodiversity. Forests provide food, shelter, and nesting environments for numerous species, and deliver multiple ecosystem services. It has been widely recognised that forest vegetation structure and its complexity influence local variations in biodiversity. As forests are facing threats globally caused by human activities, there is a need to map the biodiversity of these ecosystems. The main objective of this review was to summarise the use of airborne laser scanning (ALS) data in biodiversity-related assessment of forests. We draw attention to topics related to animal ecology, structural diversity, dead wood, fragmentation and forest habitat classification. After conducting a thorough literature search, we categorised scientific articles based on their topics, which served as the basis for the section division in this paper. The majority of the research was found to be conducted in Europe and North America, only a small fraction of the study areas was located elsewhere. Topics that have received the most attention were related to animal ecology (namely richness and diversity of forest fauna), assessment of dead trees and tree species diversity measures. Not all studies used ALS data only, as it were often fused with other remote sensing data โ€“ especially with aerial or satellite images. The fusion of spectral information from optical images and the structural information provided by ALS was highly advantageous in studies where tree species were considered. Relevant ALS variables were found to be case-specific, so variables varied widely between forest biodiversity studies. We found that there was a lack of research in geographical areas and forest types other than temperate and boreal forests. Also, topics that considered functional diversity, community composition and the effect of spatial resolution at which ALS data and field information are linked, were covered to much lesser extent

    Forest Aboveground Biomass Estimation Using Multi-Source Remote Sensing Data in Temperate Forests

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    Forests are a crucial part of global ecosystems. Accurately estimating aboveground biomass (AGB) is important in many applications including monitoring carbon stocks, investigating forest degradation, and designing sustainable forest management strategies. Remote sensing techniques have proved to be a cost-effective way to estimate forest AGB with timely and repeated observations. This dissertation investigated the use of multiple remotely sensed datasets for forest AGB estimation in temperate forests. We compared the performance of Landsat and lidar dataโ€”individually and fusedโ€”for estimating AGB using multiple regression models (MLR), Random Forest (RF) and Geographically Weight Regression (GWR). Our approach showed MLR performed similarly to GWR and both were better than RF. Integration of lidar and Landsat inputs outperformed either data source alone. However, although lidar provides valuable three-dimensional forest structure information, acquiring comprehensive lidar coverage is often cost prohibitive. Thus we developed a lidar sampling framework to support AGB estimation from Landsat images. We compared two sampling strategiesโ€”systematic and classification-basedโ€”and found that the systematic sampling selection method was highly dependent on site conditions and had higher model variability. The classification-based lidar sampling strategy was easy to apply and provides a framework that is readily transferable to new study sites. The performance of Sentinel-2 and Landsat 8 data for quantifying AGB in a temperate forest using RF regression was also tested. We modeled AGB using three datasets: Sentinel-2, Landsat 8, and a pseudo dataset that retained the spatial resolution of Sentinel-2 but only the spectral bands that matched those on Landsat 8. We found that while RF model parameters impact model outcomes, it is more important to focus attention on variable selection. Our results showed that the incorporation of red-edge information increased AGB estimation accuracy by approximately 6%. The additional spatial resolution improved accuracy by approximately 3%. The variable importance ranks in the RF regression model showed that in addition to the red- edge bands, the shortwave infrared bands were important either individually (in the Sentinel-2 model) or in band indices. With the growing availability of remote sensing datasets, developing tools to appropriately and efficiently apply remote sensing data is increasingly important

    ๋‹ค์ค‘ ์„ผ์‹ฑ ํ”Œ๋žซํผ๊ณผ ๋”ฅ๋Ÿฌ๋‹์„ ํ™œ์šฉํ•œ ๋„์‹œ ๊ทœ๋ชจ์˜ ์ˆ˜๋ชฉ ๋งตํ•‘ ๋ฐ ์ˆ˜์ข… ํƒ์ง€

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    ํ•™์œ„๋…ผ๋ฌธ(์„์‚ฌ) -- ์„œ์šธ๋Œ€ํ•™๊ต๋Œ€ํ•™์› : ๋†์—…์ƒ๋ช…๊ณผํ•™๋Œ€ํ•™ ์ƒํƒœ์กฐ๊ฒฝยท์ง€์—ญ์‹œ์Šคํ…œ๊ณตํ•™๋ถ€(์ƒํƒœ์กฐ๊ฒฝํ•™), 2023. 2. ๋ฅ˜์˜๋ ฌ.Precise estimation of the number of trees and individual tree location with species information all over the city forms solid foundation for enhancing ecosystem service. However, mapping individual trees at the city scale remains challenging due to heterogeneous patterns of urban tree distribution. Here, we present a novel framework for merging multiple sensing platforms with leveraging various deep neural networks to produce a fine-grained urban tree map. We performed mapping trees and detecting species by relying only on RGB images taken by multiple sensing platforms such as airborne, citizens and vehicles, which fueled six deep learning models. We divided the entire process into three steps, since each platform has its own strengths. First, we produced individual tree location maps by converting the central points of the bounding boxes into actual coordinates from airborne imagery. Since many trees were obscured by the shadows of the buildings, we applied Generative Adversarial Network (GAN) to delineate hidden trees from the airborne images. Second, we selected tree bark photos collected by citizen for species mapping in urban parks and forests. Species information of all tree bark photos were automatically classified after non-tree parts of images were segmented. Third, we classified species of roadside trees by using a camera mounted on a car to augment our species mapping framework with street-level tree data. We estimated the distance from a car to street trees from the number of lanes detected from the images. Finally, we assessed our results by comparing it with Light Detection and Ranging (LiDAR), GPS and field data. We estimated over 1.2 million trees existed in the city of 121.04 kmยฒ and generated more accurate individual tree positions, outperforming the conventional field survey methods. Among them, we detected the species of more than 63,000 trees. The most frequently detected species was Prunus yedoensis (21.43 %) followed by Ginkgo biloba (19.44 %), Zelkova serrata (18.68 %), Pinus densiflora (7.55 %) and Metasequoia glyptostroboides (5.97 %). Comprehensive experimental results demonstrate that tree bark photos and street-level imagery taken by citizens and vehicles are conducive to delivering accurate and quantitative information on the distribution of urban tree species.๋„์‹œ ์ „์—ญ์— ์กด์žฌํ•˜๋Š” ๋ชจ๋“  ์ˆ˜๋ชฉ์˜ ์ˆซ์ž์™€ ๊ฐœ๋ณ„ ์œ„์น˜, ๊ทธ๋ฆฌ๊ณ  ์ˆ˜์ข… ๋ถ„ํฌ๋ฅผ ์ •ํ™•ํ•˜๊ฒŒ ํŒŒ์•…ํ•˜๋Š” ๊ฒƒ์€ ์ƒํƒœ๊ณ„ ์„œ๋น„์Šค๋ฅผ ํ–ฅ์ƒ์‹œํ‚ค๊ธฐ ์œ„ํ•œ ํ•„์ˆ˜์กฐ๊ฑด์ด๋‹ค. ํ•˜์ง€๋งŒ, ๋„์‹œ์—์„œ๋Š” ์ˆ˜๋ชฉ์˜ ๋ถ„ํฌ๊ฐ€ ๋งค์šฐ ๋ณต์žกํ•˜๊ธฐ ๋•Œ๋ฌธ์— ๊ฐœ๋ณ„ ์ˆ˜๋ชฉ์„ ๋งตํ•‘ํ•˜๋Š” ๊ฒƒ์€ ์–ด๋ ค์› ๋‹ค. ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š”, ์—ฌ๋Ÿฌ๊ฐ€์ง€ ์„ผ์‹ฑ ํ”Œ๋žซํผ์„ ์œตํ•ฉํ•จ๊ณผ ๋™์‹œ์— ๋‹ค์–‘ํ•œ ๋”ฅ๋Ÿฌ๋‹ ๋„คํŠธ์›Œํฌ๋“ค์„ ํ™œ์šฉํ•˜์—ฌ ์„ธ๋ฐ€ํ•œ ๋„์‹œ ์ˆ˜๋ชฉ ์ง€๋„๋ฅผ ์ œ์ž‘ํ•˜๋Š” ์ƒˆ๋กœ์šด ํ”„๋ ˆ์ž„์›Œํฌ๋ฅผ ์ œ์•ˆํ•œ๋‹ค. ์šฐ๋ฆฌ๋Š” ์˜ค์ง ํ•ญ๊ณต์‚ฌ์ง„, ์‹œ๋ฏผ, ์ฐจ๋Ÿ‰ ๋“ฑ์˜ ํ”Œ๋žซํผ์œผ๋กœ๋ถ€ํ„ฐ ์ˆ˜์ง‘๋œ RGB ์ด๋ฏธ์ง€๋งŒ์„ ์‚ฌ์šฉํ•˜์˜€์œผ๋ฉฐ, 6๊ฐ€์ง€ ๋”ฅ๋Ÿฌ๋‹ ๋ชจ๋ธ์„ ํ™œ์šฉํ•˜์—ฌ ์ˆ˜๋ชฉ์„ ๋งตํ•‘ํ•˜๊ณ  ์ˆ˜์ข…์„ ํƒ์ง€ํ•˜์˜€๋‹ค. ๊ฐ๊ฐ์˜ ํ”Œ๋žซํผ์€ ์ €๋งˆ๋‹ค์˜ ๊ฐ•์ ์ด ์žˆ๊ธฐ ๋•Œ๋ฌธ์— ์ „ ๊ณผ์ •์„ ์„ธ ๊ฐ€์ง€ ์Šคํ…์œผ๋กœ ๊ตฌ๋ถ„ํ•  ์ˆ˜ ์žˆ๋‹ค. ์ฒซ์งธ, ์šฐ๋ฆฌ๋Š” ํ•ญ๊ณต์‚ฌ์ง„ ์ƒ์—์„œ ํƒ์ง€๋œ ์ˆ˜๋ชฉ์˜ ๋”ฅ๋Ÿฌ๋‹ ๋ฐ”์šด๋”ฉ ๋ฐ•์Šค๋กœ๋ถ€ํ„ฐ ์ค‘์‹ฌ์ ์„ ์ถ”์ถœํ•˜์—ฌ ๊ฐœ๋ณ„ ์ˆ˜๋ชฉ์˜ ์œ„์น˜ ์ง€๋„๋ฅผ ์ œ์ž‘ํ•˜์˜€๋‹ค. ๋งŽ์€ ์ˆ˜๋ชฉ์ด ๋„์‹œ ๋‚ด ๊ณ ์ธต ๋นŒ๋”ฉ์˜ ๊ทธ๋ฆผ์ž์— ์˜ํ•ด ๊ฐ€๋ ค์กŒ๊ธฐ ๋•Œ๋ฌธ์—, ์šฐ๋ฆฌ๋Š” ์ƒ์ •์  ์ ๋Œ€์  ์‹ ๊ฒฝ๋ง (Generative Adversarial Network, GAN)์„ ํ†ตํ•ด ํ•ญ๊ณต์‚ฌ์ง„ ์ƒ์— ์ˆจ๊ฒจ์ง„ ์ˆ˜๋ชฉ์„ ๊ทธ๋ ค๋‚ด๊ณ ์ž ํ•˜์˜€๋‹ค. ๋‘˜์งธ, ์šฐ๋ฆฌ๋Š” ์‹œ๋ฏผ๋“ค์ด ์ˆ˜์ง‘ํ•œ ์ˆ˜๋ชฉ์˜ ์ˆ˜ํ”ผ ์‚ฌ์ง„์„ ํ™œ์šฉํ•˜์—ฌ ๋„์‹œ ๊ณต์› ๋ฐ ๋„์‹œ ์ˆฒ ์ผ๋Œ€์— ์ˆ˜์ข… ์ •๋ณด๋ฅผ ๋งตํ•‘ํ•˜์˜€๋‹ค. ์ˆ˜ํ”ผ ์‚ฌ์ง„์œผ๋กœ๋ถ€ํ„ฐ์˜ ์ˆ˜์ข… ์ •๋ณด๋Š” ๋”ฅ๋Ÿฌ๋‹ ๋„คํŠธ์›Œํฌ์— ์˜ํ•ด ์ž๋™์œผ๋กœ ๋ถ„๋ฅ˜๋˜์—ˆ์œผ๋ฉฐ, ์ด ๊ณผ์ •์—์„œ ์ด๋ฏธ์ง€ ๋ถ„ํ•  ๋ชจ๋ธ ๋˜ํ•œ ์ ์šฉ๋˜์–ด ๋”ฅ๋Ÿฌ๋‹ ๋ถ„๋ฅ˜ ๋ชจ๋ธ์ด ์˜ค๋กœ์ง€ ์ˆ˜ํ”ผ ๋ถ€๋ถ„์—๋งŒ ์ง‘์ค‘ํ•  ์ˆ˜ ์žˆ๋„๋ก ํ•˜์˜€๋‹ค. ์…‹์งธ, ์šฐ๋ฆฌ๋Š” ์ฐจ๋Ÿ‰์— ํƒ‘์žฌ๋œ ์นด๋ฉ”๋ผ๋ฅผ ํ™œ์šฉํ•˜์—ฌ ๋„๋กœ๋ณ€ ๊ฐ€๋กœ์ˆ˜์˜ ์ˆ˜์ข…์„ ํƒ์ง€ํ•˜์˜€๋‹ค. ์ด ๊ณผ์ •์—์„œ ์ฐจ๋Ÿ‰์œผ๋กœ๋ถ€ํ„ฐ ๊ฐ€๋กœ์ˆ˜๊นŒ์ง€์˜ ๊ฑฐ๋ฆฌ ์ •๋ณด๊ฐ€ ํ•„์š”ํ•˜์˜€๋Š”๋ฐ, ์šฐ๋ฆฌ๋Š” ์ด๋ฏธ์ง€ ์ƒ์˜ ์ฐจ์„  ๊ฐœ์ˆ˜๋กœ๋ถ€ํ„ฐ ๊ฑฐ๋ฆฌ๋ฅผ ์ถ”์ •ํ•˜์˜€๋‹ค. ๋งˆ์ง€๋ง‰์œผ๋กœ, ๋ณธ ์—ฐ๊ตฌ ๊ฒฐ๊ณผ๋Š” ๋ผ์ด๋‹ค (Light Detection and Ranging, LiDAR)์™€ GPS ์žฅ๋น„, ๊ทธ๋ฆฌ๊ณ  ํ˜„์žฅ ์ž๋ฃŒ์— ์˜ํ•ด ํ‰๊ฐ€๋˜์—ˆ๋‹ค. ์šฐ๋ฆฌ๋Š” 121.04 kmยฒ ๋ฉด์ ์˜ ๋Œ€์ƒ์ง€ ๋‚ด์— ์•ฝ 130๋งŒ์—ฌ ๊ทธ๋ฃจ์˜ ์ˆ˜๋ชฉ์ด ์กด์žฌํ•˜๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€์œผ๋ฉฐ, ๋‹ค์–‘ํ•œ ์„ ํ–‰์—ฐ๊ตฌ๋ณด๋‹ค ๋†’์€ ์ •ํ™•๋„์˜ ๊ฐœ๋ณ„ ์ˆ˜๋ชฉ ์œ„์น˜ ์ง€๋„๋ฅผ ์ œ์ž‘ํ•˜์˜€๋‹ค. ํƒ์ง€๋œ ๋ชจ๋“  ์ˆ˜๋ชฉ ์ค‘ ์•ฝ 6๋งŒ 3์ฒœ์—ฌ ๊ทธ๋ฃจ์˜ ์ˆ˜์ข… ์ •๋ณด๊ฐ€ ํƒ์ง€๋˜์—ˆ์œผ๋ฉฐ, ์ด์ค‘ ๊ฐ€์žฅ ๋นˆ๋ฒˆํžˆ ํƒ์ง€๋œ ์ˆ˜๋ชฉ์€ ์™•๋ฒš๋‚˜๋ฌด (Prunus yedoensis, 21.43 %)์˜€๋‹ค. ์€ํ–‰๋‚˜๋ฌด (Ginkgo biloba, 19.44 %), ๋Šํ‹ฐ๋‚˜๋ฌด (Zelkova serrata, 18.68 %), ์†Œ๋‚˜๋ฌด (Pinus densiflora, 7.55 %), ๊ทธ๋ฆฌ๊ณ  ๋ฉ”ํƒ€์„ธ์ฟผ์ด์–ด (Metasequoia glyptostroboides, 5.97 %) ๋“ฑ์ด ๊ทธ ๋’ค๋ฅผ ์ด์—ˆ๋‹ค. ํฌ๊ด„์ ์ธ ๊ฒ€์ฆ์ด ์ˆ˜ํ–‰๋˜์—ˆ๊ณ , ๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š” ์‹œ๋ฏผ์ด ์ˆ˜์ง‘ํ•œ ์ˆ˜ํ”ผ ์‚ฌ์ง„๊ณผ ์ฐจ๋Ÿ‰์œผ๋กœ๋ถ€ํ„ฐ ์ˆ˜์ง‘๋œ ๋„๋กœ๋ณ€ ์ด๋ฏธ์ง€๋Š” ๋„์‹œ ์ˆ˜์ข… ๋ถ„ํฌ์— ๋Œ€ํ•œ ์ •ํ™•ํ•˜๊ณ  ์ •๋Ÿ‰์ ์ธ ์ •๋ณด๋ฅผ ์ œ๊ณตํ•œ๋‹ค๋Š” ๊ฒƒ์„ ๊ฒ€์ฆํ•˜์˜€๋‹ค.1. Introduction 6 2. Methodology 9 2.1. Data collection 9 2.2. Deep learning overall 12 2.3. Tree counting and mapping 15 2.4. Tree species detection 16 2.5. Evaluation 21 3. Results 22 3.1. Evaluation of deep learning performance 22 3.2. Tree counting and mapping 23 3.3. Tree species detection 27 4. Discussion 30 4.1. Multiple sensing platforms for urban areas 30 4.2. Potential of citizen and vehicle sensors 34 4.3. Implications 48 5. Conclusion 51 Bibliography 52 Abstract in Korean 61์„

    Ash Tree Identification Based on the Integration of Hyperspectral Imagery and High-density Lidar Data

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    Monitoring and management of ash trees has become particularly important in recent years due to the heightened risk of attack from the invasive pest, the emerald ash borer (EAB). However, distinguishing ash from other deciduous trees can be challenging. Both hyperspectral imagery and Light detection and ranging (LiDAR) data are two valuable data sources that are often used for tree species classification. Hyperspectral imagery measures detailed spectral reflectance related to the biochemical properties of vegetation, while LiDAR data measures the three-dimensional structure of tree crowns related to morphological characteristics. Thus, the accuracy of vegetation classification may be improved by combining both techniques. Therefore, the objective of this research is to integrate hyperspectral imagery and LiDAR data for improving ash tree identification. Specifically, the research aims include: 1) using LiDAR data for individual tree crowns segmentation; 2) using hyperspectral imagery for extraction of relative pure crown spectra; 3) fusing hyperspectral and LiDAR data for ash tree identification. It is expected that the classification accuracy of ash trees will be significantly improved with the integration of hyperspectral and LiDAR techniques. Analysis results suggest that, first, 3D crown structures of individual trees can be reconstructed using a set of generalized geometric models which optimally matched LiDAR-derived raster image, and crown widths can be further estimated using tree height and shape-related parameters as independent variables and ground measurement of crown widths as dependent variables. Second, with constrained linear spectral mixture analysis method, the fractions of all materials within a pixel can be extracted, and relative pure crown-scale spectra can be further calculated using illuminated-leaf fraction as weighting factors for tree species classification. Third, both crown shape index (SI) and coefficient of variation (CV) can be extracted from LiDAR data as invariant variables in treeโ€™s life cycle, and improve ash tree identification by integrating with pixel-weighted crown spectra. Therefore, three major contributions of this research have been made in the field of tree species classification:1) the automatic estimation of individual tree crown width from LiDAR data by combining a generalized geometric model and a regression model, 2) the computation of relative pure crown-scale spectral reflectance using a pixel-weighting algorithm for tree species classification, 3) the fusion of shape-related structural features and pixel-weighted crown-scale spectral features for improving of ash tree identification

    A multiscale remote sensing assessment of subtropical indigenous forests along the wild coast, South Africa

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    The subtropical forests located along South Africaโ€™s Wild Coast region, declared as one of the biodiversity hotspots, provide benefits to the local and national economy. However, there is evidence of increased pressure exerted on the forests by growing population and reduced income from activities not related to forest products. The ability of remote sensing to quantify subtropical forest changes over time, perform species discrimination (using field spectroscopy) and integrating field spectral and multispectral data were all assessed in this study. Investigations were conducted at pixel, leaf and sub-pixel levels. Both per-pixel and sub-pixel classification methods were used for improved forest characterisation. Using SPOT 6 imagery for 2013, the study determined the best classification algorithm for mapping sub-tropical forest and other land cover types to be the maximum likelihood classifier. Maximum likelihood outperformed minimum distance, spectral angle mapper and spectral information divergence algorithms, based on overall accuracy and Kappa coefficient values. Forest change analysis was made based on spectral measurements made at top of the atmosphere (TOC) level. When applied to the 2005 and 2009 SPOT 5 images, subtropical forest changes between 2005-2009 and 2009-2013 were quantified. A temporal analysis of forest cover trends in the periods 2005-2009 and 2009-2013 identified a decreasing trend of -3648.42 and -946.98 ha respectively, which translated to 7.81 percent and 2.20 percent decrease. Although there is evidence of a trend towards decreased rates of forest loss, more conservation efforts are required to protect the Wild Coast ecosystem. Using field spectral measurements data, the hierarchical method (comprising One-way ANOVA with Bonferroni correction, Classification and Regression Trees (CART) and Jeffries Matusita method) successfully selected optimal wavelengths for species discrimination at leaf level. Only 17 out of 2150 wavelengths were identified, thereby reducing the complexities related to data dimensionality. The optimal 17 wavelength bands were noted in the visible (438, 442, 512 and 695 nm), near infrared (724, 729, 750, 758, 856, 936, 1179, 1507 and 1673 nm) and mid-infrared (2220, 2465, 2469 and 2482 nm) portions of the electromagnetic spectrum. The Jeffries-Matusita (JM) distance method confirmed the separability of the selected wavelength bands. Using these 17 wavelengths, linear discriminant analysis (LDA) classified subtropical species at leaf level more accurately than partial least squares discriminant analysis (PLSDA) and random forest (RF). In addition, the study integrated field-collected canopy spectral and multispectral data to discriminate proportions of semi-deciduous and evergreen subtropical forests at sub-pixel level. By using the 2013 land cover (using MLC) to mask non-forested portions before sub-pixel classification (using MTMF), the proportional maps were a product of two classifiers. The proportional maps show higher proportions of evergreen forests along the coast while semi-deciduous subtropical forest species were mainly on inland parts of the Wild Coast. These maps had high accuracy, thereby proving the ability of an integration of field spectral and multispectral data in mapping semi-deciduous and evergreen forest species. Overall, the study has demonstrated the importance of the MLC and LDA and served to integrate field spectral and multispectral data in subtropical forest characterisation at both leaf and top-of-atmosphere levels. The success of both the MLC and LDA further highlighted how essential parametric classifiers are in remote sensing forestry applications. Main subtropical characteristics highlighted in this study were species discrimination at leaf level, quantifying forest change at pixel level and discriminating semi-deciduous and evergreen forests at sub-pixel level
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