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Keywords = kauri dieback disease

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20 pages, 3991 KiB  
Article
Phytophthora Communities Associated with Agathis australis (kauri) in Te Wao Nui o Tiriwa/Waitākere Ranges, New Zealand
by Shannon Hunter, Ian Horner, Jack Hosking, Ellena Carroll, Jayne Newland, Matthew Arnet, Nick Waipara, Bruce Burns, Peter Scott and Nari Williams
Forests 2024, 15(5), 735; https://doi.org/10.3390/f15050735 - 23 Apr 2024
Cited by 1 | Viewed by 1285
Abstract
Studies of Phytophthora impact in forests generally focus on individual species without recognition that Phytophthora occur in multispecies communities. This study investigated community structure of Phytophthora species in the rhizosphere of Agathis australis (kauri) in Te Wao Nui o Tiriwa/Waitākere Ranges, New Zealand, [...] Read more.
Studies of Phytophthora impact in forests generally focus on individual species without recognition that Phytophthora occur in multispecies communities. This study investigated community structure of Phytophthora species in the rhizosphere of Agathis australis (kauri) in Te Wao Nui o Tiriwa/Waitākere Ranges, New Zealand, in the context of kauri dieback disease expression. Soil sampling and tree monitoring were conducted on 767 randomly selected mature kauri trees. Phytophthora species were detected using both soil baiting and DNA metabarcoding of environmental DNA (eDNA). Four species were detected with soil baiting (P. agathidicida, P. cinnamomi, P. multivora, and P. pseudocryptogea/P. cryptogea) and an additional three species with metabarcoding (P. kernoviae, P. cactorum/P. aleatoria and an unknown clade 7 species). Phytophthora cinnamomi was the most abundant species and was distributed throughout the forest. Both P. multivora and P. agathidicida were limited to forest edges, suggesting more recent introductions. P. agathidicida presence was strongly correlated with declining canopy health, confirming its role as the main driver of kauri dieback. The limited distribution of P. agathidicida and infrequent detections (11.0% samples) suggests that that this species is spreading as an introduced invasive pathogen and provide hope that with strategic management (including track upgrades and closures, restricting access to uninfected areas, and continual monitoring) uninfected areas of the forest can be protected. The frequent detections of P. cinnamomi and P. multivora from symptomatic trees in the absence of P. agathidicida suggest more research is needed to understand their roles in kauri forest health. Full article
(This article belongs to the Section Forest Ecology and Management)
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Figure 1

Figure 1
<p>Location of the 767 soil samples (represented by red circles) collected in the Waitākere Ranges Regional Park survey for the current study. The smaller map on the left shows the location of the Waitākere Ranges Regional Park in relation to Auckland City on the upper North Island of New Zealand.</p>
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<p>The number of sequences produced for <span class="html-italic">Phytophthora agathidicida</span> (blue with solid line), <span class="html-italic">P. cinnamomi</span> (pink with short dashes), and <span class="html-italic">P. pseudocryptogea</span> (green with long dashes) in the mock community samples with known DNA concentrations. Each line represents the best-fit line from the negative binomial generalised linear model (made using the R package MASS version 7.3.60) for each species and the surrounding shaded areas indicate 95% confidence intervals (CI). <span class="html-italic">Phytophthora multivora</span> was omitted due to lack of sequence reads.</p>
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<p>A phylogram based on ITS1 gene sequence data indicating the placement of the two clade 7 species detected in this study in relation to closely related taxa. <span class="html-italic">Phytophthora cinnamomi</span> represented by ASV1_extraction and <span class="html-italic">Phytophthora</span> sp. unknown represented by ASV10_extraction. The sequences were trimmed to the ITS1 gene region and compared with the curated ITS1 gene database supplied by Professor Treena Burgess (Harry Butler Institute, Murdoch University, Murdoch, WA, Australia). Numbers above the branch represent the bootstrap support based on parsimony analysis.</p>
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<p>Venn Diagrams (created using the R package eulerr) showing the number of positive samples for <span class="html-italic">Phytophthora cinnamomi</span>, <span class="html-italic">P. agathidicida</span>, and <span class="html-italic">P. multivora</span> using either baiting or ITS metabarcoding.</p>
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<p>Distribution of the three key species, <span class="html-italic">Phytophthora cinnamomi</span> (pink), <span class="html-italic">P. agathidicida</span> (blue), and <span class="html-italic">P. multivora</span> (yellow), across the Waitākere Ranges Regional Park, New Zealand. The grey circles indicate the position of samples in which the relevant <span class="html-italic">Phytophthora</span> species was not detected. Created in ARC GIS Pro version 2.7.1. The scale bar is 4 km.</p>
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<p>Co-occurrence of <span class="html-italic">Phytophthora cinnamomi</span> (pink), <span class="html-italic">P. agathidicida</span> (blue), and <span class="html-italic">P. multivora</span> (yellow) in the sampled kauri trees which were asymptomatic for kauri dieback (canopy score less than 3; n = 595) or symptomatic (canopy dieback score ≥ 3 and/or the presence of a basal bleed; n = 172). Positive detections with either baiting or ITS metabarcoding. There was one asymptomatic sample positive for <span class="html-italic">P. agathidicida</span> and <span class="html-italic">P. multivora</span> only, shown by the ‘1’ outside the Venn diagram with a directional line.</p>
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<p><span class="html-italic">Phytophthora agathidicida</span> (blue with solid line), <span class="html-italic">P. cinnamomi</span> (pink with short dashes), and <span class="html-italic">P. multivora</span> (yellow with long dashes) presence in kauri soil samples in association with canopy dieback scores (score of 0 = healthy tree, score of 5 = dead tree). Solid lines and surrounding grey areas indicate the fits and 95% confidence intervals (CI) from binomial generalised linear models (NBGLM) created in R with the package stats.</p>
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17 pages, 2729 KiB  
Article
Cross-Cultural Leadership Enables Collaborative Approaches to Management of Kauri Dieback in Aotearoa New Zealand
by Lee Hill, Edward Ashby, Nick Waipara, Robin Taua-Gordon, Aleesha Gordon, Fredrik Hjelm, Stanley E. Bellgard, Emma Bodley and Linley K. Jesson
Forests 2021, 12(12), 1671; https://doi.org/10.3390/f12121671 - 30 Nov 2021
Cited by 16 | Viewed by 3815
Abstract
In Aotearoa/New Zealand, the soilborne pathogen Phytophthora agathidicida threatens the survival of the iconic kauri, and the ecosystem it supports. In 2011, a surveillance project to identify areas of kauri dieback caused by Phytophthora agathidicida within the Waitākere Ranges Regional Park (WRRP) highlighted [...] Read more.
In Aotearoa/New Zealand, the soilborne pathogen Phytophthora agathidicida threatens the survival of the iconic kauri, and the ecosystem it supports. In 2011, a surveillance project to identify areas of kauri dieback caused by Phytophthora agathidicida within the Waitākere Ranges Regional Park (WRRP) highlighted the potential impact of the pathogen. A repeat of the surveillance in 2015/16 identified that approximately a quarter of the kauri area within the Regional Park was infected or possibly infected, an increase from previous surveys. The surveillance program mapped 344 distinct kauri areas and showed that 33.4% of the total kauri areas were affected or potentially affected by kauri dieback and over half (58.3%) of the substantial kauri areas (above 5 ha in size) were showing symptoms of kauri dieback. Proximity analysis showed 71% of kauri dieback zones to be within 50 m of the track network. Spatial analysis showed significantly higher proportions of disease presence along the track network compared to randomly generated theoretical track networks. Results suggest that human interaction is assisting the transfer of Phytophthora agathidicida within the area. The surveillance helped trigger the declaration of a cultural ban (rāhui) on recreational access. Te Kawerau ā Maki, the iwi of the area, placed a rāhui over the kauri forest eco-system of the Waitākere Forest (Te Wao Nui o Tiriwa) in December 2017. The purpose of the rāhui was to help prevent the anthropogenic spread of kauri dieback, to provide time for investment to be made into a degraded forest infrastructure and for research to be undertaken, and to help protect and support forest health (a concept encapsulated by the term mauri). Managing the spread and impact of the pathogen remains an urgent priority for this foundation species in the face of increasing pressures for recreational access. Complimentary quantitative and qualitative research programs into track utilization and ecologically sensitive design, collection of whakapapa seed from healthy and dying trees, and remedial phosphite treatments are part of the cross-cultural and community-enabled biosecurity initiatives to Kia Toitu He Kauri “Keep Kauri Standing”. Full article
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Figure 1
<p>Interpretive display of simulated track analysis, with distances measured of the Kauri dieback zone (distance a), possible kauri dieback zone (distance b) and non-symptomatic kauri zone (distance c).</p>
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<p>Change in percentage of kauri area affected by kauri dieback within the Waitākere Ranges Regional Park (WRRP) between 2010 and 2015/16.</p>
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<p>Presence of kauri dieback within distinct kauri areas within the WRRP highlighting that larger blocks of kauri have higher levels of kauri dieback.</p>
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<p>Percentage distribution of kauri dieback and possible kauri dieback zones to the track network within the WRRP.</p>
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<p>Comparison of dieback along tracks (km) between actual data from this survey and simulated tracks of the same length showing that dieback is more likely to be nearer tracks. Black lines are the 99% CIs from the simulated tracks.</p>
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<p>Comparison of dieback along tracks (percentage) between actual data from this survey and simulated tracks of the same length showing dieback is more likely to be nearer tracks. Black lines are the 99% CIs from the simulated tracks.</p>
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32 pages, 12906 KiB  
Article
Stress Detection in New Zealand Kauri Canopies with WorldView-2 Satellite and LiDAR Data
by Jane J. Meiforth, Henning Buddenbaum, Joachim Hill, James D. Shepherd and John R. Dymond
Remote Sens. 2020, 12(12), 1906; https://doi.org/10.3390/rs12121906 - 12 Jun 2020
Cited by 7 | Viewed by 6596
Abstract
New Zealand kauri trees are threatened by the kauri dieback disease (Phytophthora agathidicida (PA)). In this study, we investigate the use of pan-sharpened WorldView-2 (WV2) satellite and Light Detection and Ranging (LiDAR) data for detecting stress symptoms in the canopy of kauri [...] Read more.
New Zealand kauri trees are threatened by the kauri dieback disease (Phytophthora agathidicida (PA)). In this study, we investigate the use of pan-sharpened WorldView-2 (WV2) satellite and Light Detection and Ranging (LiDAR) data for detecting stress symptoms in the canopy of kauri trees. A total of 1089 reference crowns were located in the Waitakere Ranges west of Auckland and assessed by fieldwork and the interpretation of aerial images. Canopy stress symptoms were graded based on five basic stress levels and further refined for the first symptom stages. The crown polygons were manually edited on a LiDAR crown height model. Crowns with a mean diameter smaller than 4 m caused most outliers with the 1.8 m pixel size of the WV2 multispectral bands, especially at the more advanced stress levels of dying and dead trees. The exclusion of crowns with a diameter smaller than 4 m increased the correlation in an object-based random forest regression from 0.85 to 0.89 with only WV2 attributes (root mean squared error (RMSE) of 0.48, mean absolute error (MAE) of 0.34). Additional LiDAR attributes increased the correlation to 0.92 (RMSE of 0.43, MAE of 0.31). A red/near-infrared (NIR) normalised difference vegetation index (NDVI) and a ratio of the red and green bands were the most important indices for an assessment of the full range of stress symptoms. For detection of the first stress symptoms, an NDVI on the red-edge and green bands increased the performance. This study is the first to analyse the use of spaceborne images for monitoring canopy stress symptoms in native New Zealand kauri forest. The method presented shows promising results for a cost-efficient stress monitoring of kauri crowns over large areas. It will be tested in a full processing chain with automatic kauri identification and crown segmentation. Full article
(This article belongs to the Special Issue Forest Canopy Disturbance Detection Using Satellite Remote Sensing)
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Graphical abstract
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<p>Kauri crown size classes: Non-symptomatic small, medium, and large kauri crowns, as a profile on a Light Detection and Ranging (LiDAR) point cloud (<b>a–c</b>) [<a href="#B11-remotesensing-12-01906" class="html-bibr">11</a>] and on 7.5 cm aerial images below (<b>d–f</b>) [<a href="#B12-remotesensing-12-01906" class="html-bibr">12</a>].</p>
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<p>(<b>a</b>) Location of the Waitakere Ranges on the North Island of New Zealand west of Auckland City, with the natural range of kauri distribution and <span class="html-italic">Phytophthora agathidicida</span> (PA)-positive samples [<a href="#B80-remotesensing-12-01906" class="html-bibr">80</a>,<a href="#B81-remotesensing-12-01906" class="html-bibr">81</a>]. (<b>b</b>) Study sites and extent of the remote sensing datasets in the Waitakere Ranges, with the reference crowns marked in orange (background map: LINZ 2019 [<a href="#B82-remotesensing-12-01906" class="html-bibr">82</a>]).</p>
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<p>Position of WorldView-2 (WV2) bands and kauri spectra for non-symptomatic, medium, and dead crowns based on (<b>a</b>) an airborne hyperspectral image (448 spectral bands) and (<b>b</b>) the pan-sharpened WV2 multispectral bands [<a href="#B7-remotesensing-12-01906" class="html-bibr">7</a>,<a href="#B92-remotesensing-12-01906" class="html-bibr">92</a>].</p>
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<p>Aerial images from (<b>a</b>) non-symptomatic kauri, several states of decline in kauri crowns (<b>b–f</b>), to (<b>g</b>) dead trees. All crowns are of a medium size (mean diameter: 4–12.2 m) [<a href="#B12-remotesensing-12-01906" class="html-bibr">12</a>].</p>
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<p>Reference crowns in a high kauri stand (<b>a</b>) and a low stand (<b>b</b>), with symptom values from 1 = non-symptomatic to 5 = dead, on a NIR1 green-blue composite of the WorldView-2 (WV2) image.</p>
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<p>Workflow diagram for the attribute calculation.</p>
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<p>Raster datasets of selected attributes with reference crowns marked as red polygons and labelled stress symptom values. The images show a (<b>a</b>) normalised difference vegetation index (NDVI) on red and NIR1 bands (NDVI_75), (<b>b</b>) the red-green ratio index (RGRI) on the red and green bands, (<b>c</b>) a variance raster for a 5 × 5 kernel on a crown height model (CHM), and (<b>d</b>) a CHM with a freeze distance of 1 m. The grey areas on the spectral rasters (a and b) mark shadows and no-data pixels that were masked out for the analysis.</p>
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<p>Bar chart showing the absolute numbers of outliers (error &gt;1) in four crown diameter classes (total 1089) and five aggregated stress levels for a random forest (RF) regression with nine attributes in a 10-fold cross validation.</p>
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<p>A combination of jitter and boxplot diagrams for an RF regression on WV2 attributes for the seven stress levels, based on (<b>a</b>) crowns with a diameter larger than 3 m (1089) and (<b>b</b>) crowns with a diameter larger than 4 m (895).</p>
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<p>Boxplot for the predicted and actual values from an RF regression on the seven-level reference scheme for crowns with a diameter larger than 4 m (total 895). Figure (<b>a</b>) shows the basic scale from 1 to 5 and figure (<b>b</b>) presents the results after rescaling the value 5 for “dead” tree crowns to 7.</p>
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<p>Maps showing reference crowns in two forest stands in the Cascade area. The labels indicate the actual stress levels (left number) and the predicted stress levels (right number) on an NDVI background raster (bands 5, 7). The predicted values are based on the seven-level reference scheme with WV2 attributes according to <a href="#remotesensing-12-01906-t004" class="html-table">Table 4</a>.</p>
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<p>Correlations (<b>a</b>) and RMSE (<b>b</b>) of WV2 and LiDAR attributes for an RF regression on seven stress symptom levels. The performance was tested for crowns with a mean diameter larger than 3 m (light colour, total 1089) and larger than 4 m (dark colour, total 895). The RF regression was carried out in 1000 repetitions for a random three-fold split with a tree depth of eight.</p>
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<p>Different steps in the orthorectification illustrated with the PAN channel of the WorldView-2 image, for a forest section in the Cascade area. The red polygons mark crowns of kauri and dead/dying trees that were used in the analysis. The 10% buffer, which was removed for the analysis, is marked with a stippled line. The orange polygons mark crowns from other species and kauri smaller than 3 m diameter that were not used in this study.</p>
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<p>Spatial offset of crown polygons, edited on the LiDAR CHM, to the WorldView-2 image, measured for 100 randomly selected crowns. The offset is marked in classes with (<b>a</b>) the distance in percent from the crown diameter and (<b>b</b>) the absolute distance in meter. The blue values mark the offset for the full crown polygons, and the green values mark the offset for the inner buffer that was used in the analysis, after a 10% outer buffer was removed.</p>
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33 pages, 12246 KiB  
Article
Monitoring of Canopy Stress Symptoms in New Zealand Kauri Trees Analysed with AISA Hyperspectral Data
by Jane J. Meiforth, Henning Buddenbaum, Joachim Hill and James Shepherd
Remote Sens. 2020, 12(6), 926; https://doi.org/10.3390/rs12060926 - 13 Mar 2020
Cited by 13 | Viewed by 5541
Abstract
The endemic New Zealand kauri trees (Agathis australis) are under threat by the deadly kauri dieback disease (Phytophthora agathidicida (PA)). This study aimed to identify spectral index combinations for characterising visible stress symptoms in the kauri canopy. The analysis is [...] Read more.
The endemic New Zealand kauri trees (Agathis australis) are under threat by the deadly kauri dieback disease (Phytophthora agathidicida (PA)). This study aimed to identify spectral index combinations for characterising visible stress symptoms in the kauri canopy. The analysis is based on an aerial AISA hyperspectral image mosaic and 1258 reference crowns in three study sites in the Waitakere Ranges west of Auckland. A field-based assessment scheme for canopy stress symptoms (classes 1–5) was further optimised for use with RGB aerial images. A combination of four indices with six bands in the spectral range 450–1205 nm resulted in a correlation of 0.93 (mean absolute error 0.27, RMSE 0.48) for all crown sizes. Comparable results were achieved with five indices in the 450–970 nm region. A Random Forest (RF) regression gave the most accurate predictions while a M5P regression tree performed nearly as well and a linear regression resulted in slightly lower correlations. Normalised Difference Vegetation Indices (NDVI) in the near-infrared / red spectral range were the most important index combinations, followed by indices with bands in the near-infrared spectral range from 800 to 1205 nm. A test on different crown sizes revealed that stress symptoms in smaller crowns with denser foliage are best described in combination with pigment-sensitive indices that include bands in the green and blue spectral range. A stratified approach with individual models for pre-segmented low and high forest stands improved the overall performance. The regression models were also tested in a pixel-based analysis. A manual interpretation of the resulting raster map with stress symptom patterns observed in aerial imagery indicated a good match. With bandwidths of 10 nm and a maximum number of six bands, the selected index combinations can be used for large-area monitoring on an airborne multispectral sensor. This study establishes the base for a cost-efficient, objective monitoring method for stress symptoms in kauri canopies, suitable to cover large forest areas with an airborne multispectral sensor. Full article
(This article belongs to the Special Issue Hyperspectral Remote Sensing for Biodiversity Mapping)
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Graphical abstract
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<p>Kauri growth classes used in this study, according to the mean crown diameter (cdm) [<a href="#B11-remotesensing-12-00926" class="html-bibr">11</a>]. (Photos [<a href="#B12-remotesensing-12-00926" class="html-bibr">12</a>]).</p>
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<p>Mature kauri stand in different foliage colour variations in the Waitakere Ranges shown in (<b>a</b>) oblique view and (<b>b</b>) nadir view [<a href="#B13-remotesensing-12-00926" class="html-bibr">13</a>].</p>
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<p>Study sites in the Waitakere Ranges with the reference crowns marked in orange. The labels give the name of the area and the size in square kilometres. Small map: Location of the Waitakere Ranges on the North Island of New Zealand, west of Auckland City (background maps: [<a href="#B83-remotesensing-12-00926" class="html-bibr">83</a>,<a href="#B84-remotesensing-12-00926" class="html-bibr">84</a>]).</p>
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<p>Workflow for the preparation of crown-based attributes that were used in the analysis.</p>
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<p>(<b>a</b>) Crown size classes of the reference crowns (total 1258), used in the analysis per low and high forest stand situation. The crown size classes correspond to the classes used in <a href="#remotesensing-12-00926-t002" class="html-table">Table 2</a>. (<b>b</b>) Low and high forest stands were distinguished with an average height of 21 m on pre-segmented stand polygons based on a LiDAR CHM ([<a href="#B89-remotesensing-12-00926" class="html-bibr">89</a>]).</p>
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<p>Inter-crown (<b>a</b>,<b>b</b>) and within-crown (<b>c</b>,<b>d</b>) spectral variability for the sunlit part of 189 non-symptomatic small kauri crowns (crown diameter &gt; 3–4.8 m) (<b>a</b>,<b>c</b>) and 337 large kauri crowns with no visible stress symptoms (crown diameter &gt;12.8 m) (<b>b</b>,<b>d</b>). The mean spectra are marked in colour.</p>
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<p>Mean spectra (bold signatures) and standard deviation (stdev, thin signatures) of kauri in three symptom classes: Non-symptomatic (class 1, green), medium symptoms (class 3, orange) and dead trees (class 5, red). The number of pixels (pix) for the different classes is given in parentheses.</p>
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<p>Spectra of kauri in three different size classes according to their mean crown diameter (cdm) (S = small 3–4.8 m cdm, M = medium &gt;4.8–12.2 m cdm, L = large &gt;12.2 m cdm) sorted according to three symptom levels: “Non-symptomatic” (green), “medium stress symptoms” (orange) and “dead crowns” (red), which include visible undergrowth and epiphytes. For better readability, the spectra of crowns with medium symptoms and dead trees were offset by 3000 and 6000 units, respectively.</p>
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<p>Combined box- and jitter-plot diagrams of the predicted values versus the actual reference crown values for crowns in all sizes classes. Figure (<b>a</b>) shows the results of the original scale from 1 = “non-symptomatic” to 5 = “dead”. Figure (<b>b</b>) shows the results for a rescaled range, with the former value 5 for dead trees changed to value 8. The analysis is based on a RF regression with 1000 iterations in a 10-fold cross-validation on the baseline 6-band index combination for the full spectral range.</p>
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<p>Resulting maps (<b>a</b>,<b>c</b>,<b>e</b>) and corresponding RGB aerial images (<b>b</b>,<b>d</b>,<b>f</b>) (2016) [<a href="#B89-remotesensing-12-00926" class="html-bibr">89</a>] of a pixel-based application of the baseline index combination for two forest stands with marked reference crowns and their reference symptom class values. The analysis was carried out as a Random Forest regression in the EnMAP toolbox [<a href="#B96-remotesensing-12-00926" class="html-bibr">96</a>] on selected indices rasters from the crown based model.</p>
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<p>Photo illustration of the canopy score scheme for kauri used by Auckland Council in 2015 with five classes [<a href="#B136-remotesensing-12-00926" class="html-bibr">136</a>]: 1 = Healthy crown—no visible signs of dieback, 2 = Foliage/canopy thinning, 3 = Some branch dieback, 4 = Severe dieback, 5 = Dead.</p>
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26 pages, 5947 KiB  
Article
Detection of New Zealand Kauri Trees with AISA Aerial Hyperspectral Data for Use in Multispectral Monitoring
by Jane J. Meiforth, Henning Buddenbaum, Joachim Hill, James Shepherd and David A. Norton
Remote Sens. 2019, 11(23), 2865; https://doi.org/10.3390/rs11232865 - 2 Dec 2019
Cited by 4 | Viewed by 5684
Abstract
The endemic New Zealand kauri trees (Agathis australis) are of major importance for the forests in the northern part of New Zealand. The mapping of kauri locations is required for the monitoring of the deadly kauri dieback disease (Phytophthora agathidicida [...] Read more.
The endemic New Zealand kauri trees (Agathis australis) are of major importance for the forests in the northern part of New Zealand. The mapping of kauri locations is required for the monitoring of the deadly kauri dieback disease (Phytophthora agathidicida (PTA)). In this study, we developed a method to identify kauri trees by optical remote sensing that can be applied in an area-wide campaign. Dead and dying trees were separated in one class and the remaining trees with no to medium stress symptoms were defined in the two classes “kauri” and “other”. The reference dataset covers a representative selection of 3165 precisely located crowns of kauri and 21 other canopy species in the Waitakere Ranges west of Auckland. The analysis is based on an airborne hyperspectral AISA Fenix image (437–2337 nm, 1 m2 pixel resolution). The kauri spectra show characteristically steep reflectance and absorption features in the near-infrared (NIR) region with a distinct long descent at 1215 nm, which can be parameterised with a modified Normalised Water Index (mNDWI-Hyp). With a Jeffries–Matusita separability over 1.9, the kauri spectra can be well separated from 21 other canopy vegetation spectra. The Random Forest classifier performed slightly better than Support Vector Machine. A combination of the mNDWI-Hyp index with four additional spectral indices with three red to NIR bands resulted in an overall pixel-based accuracy (OA) of 91.7% for crowns larger 3 m diameter. While the user’s and producer’s accuracies for the class “kauri” with 94.6% and 94.8% are suitable for management purposes, the separation of “dead/dying trees” from “other” canopy vegetation poses the main challenge. The OA can be improved to 93.8% by combining “kauri” and “dead/dying” trees in one class, separate classifications for low and high forest stands and a binning to 10 nm bandwidths. Additional wavelengths and their respective indices only improved the OA up to 0.6%. The method developed in this study allows an accurate location of kauri trees for an area-wide mapping with a five-band multispectral sensor in a representative selection of forest ecosystems. Full article
(This article belongs to the Section Forest Remote Sensing)
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Graphical abstract
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<p>Kauri growth classes used in this study, depending on the mean crown diameter (cdm). (Photos: [<a href="#B39-remotesensing-11-02865" class="html-bibr">39</a>]).</p>
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<p>(<b>a</b>) Location of the Waitakere Ranges on the North Island of New Zealand west of Auckland City. The general area with naturally occurring kauri in New Zealand [<a href="#B2-remotesensing-11-02865" class="html-bibr">2</a>] is marked as hatched. (<b>b</b>) Study sites in the Waitakere Ranges with the reference crowns marked in red (background map: [<a href="#B42-remotesensing-11-02865" class="html-bibr">42</a>]).</p>
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<p>Reference crowns (total 3165), used in the analysis, per class and diameter.</p>
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<p>Mean spectra of the target classes “kauri”, “dead/dying” and “other” with standard deviations (stdev).</p>
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<p>Jeffries–Matusita separability [<a href="#B61-remotesensing-11-02865" class="html-bibr">61</a>] of the three target classes for different spectral ranges. A value larger than 1.9 indicates a high separability. The analysis was based on MNF transformations for all bands in the different spectral ranges.</p>
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<p>Mean spectra of kauri (thick black line) and six selected other canopy species (grey) that got most easily confused with kauri. The number of pixels (pix) used to generate the mean spectra is given in parentheses. The spectra of these species show the lowest separability from the kauri spectrum in this study (see <a href="#remotesensing-11-02865-t0A2" class="html-table">Table A2</a>).</p>
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<p>Mean spectra of kauri (black) and five other canopy species (grey) that have the highest separabilities from the kauri spectrum in this study (see <a href="#remotesensing-11-02865-t0A2" class="html-table">Table A2</a>). The number of pixels (pix) used to generate the mean spectra is given in parentheses.</p>
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<p>Mean spectra of the target classes “kauri”, “dead/dying” and “other” with standard deviations (“stdev”). Below: Band positions of 13 selected spectral indices.</p>
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<p>Performance of selected indices and index combinations to identify the class “dead/dying” (light grey) and to distinguish between “kauri” and “other vegetation” (dark grey) with an RF classification (five-fold random split, 20 repetitions). Please note that the x-axis starts at 55%.</p>
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<p>Performance of the final 4–8-band index combinations to distinguish the three target classes “kauri”, “dead/dying” and “other” canopy vegetation. (RF, five-fold random split, 20 repetitions). Please note that the y-axis starts at 89%.</p>
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<p>RGB images of the three first bands of MNF transformations [<a href="#B49-remotesensing-11-02865" class="html-bibr">49</a>] from: (<b>a</b>) the VIS to NIR1 spectral range (431–970 nm); (<b>b</b>) VIS to NIR2 (431–1327 nm); and (<b>c</b>) the full spectral range from VIS to SWIR (431–2337 nm). The importance of the NIR2 and SWIR spectrum is visible in the higher colour contrast of kauri crowns compared to the VNIR image. The numbers in the kauri polygons indicate the stress symptom class for the crown with 1 = non-symptomatic and 5 = dead.</p>
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<p>Histograms for selected indices on sunlit pixels for all crown diameters, with the class “kauri” marked in light blue, the class “dead/dying” in red and the class “other” in dark blue. (<b>a</b>) The histogram for the mNDWI-Hyp index, which performed best to separate the class kauri from other vegetation by capturing distinctive features in the NIR2 region, is shown. For the separation of the class “dead/dying”, indices in the RED/NIR1 region are better suited, such as (<b>b</b>) the SR800 and (<b>c</b>) the NDNI index (see <a href="#remotesensing-11-02865-t0A3" class="html-table">Table A3</a> for descriptions of these indices).</p>
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<p>Overall accuracies for two selected sets of six and eight bands in the visible to NIR1 range. The accuracies are calculated for two and three target classes both with and without an additional CHM layer. The results are based on an RF classification with a three-fold split in 10 repetitions on 94,971 pixel values, including small crowns (&lt;3 m diameter). The standard deviations vary from 0.12 to 0.2.</p>
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<p>Combined results of 10 RF classifications with a 5-fold stratified random split with different seed values. Overview (left) and detailed maps (right) for the Cascades (<b>a</b>,<b>b</b>), Maungaroa (<b>c</b>,<b>d</b>) and Kauri Grove area (<b>e</b>,<b>f</b>). The numbers indicate the symptom classes in kauri crowns (1 = non-symptomatic, 5 = dead).</p>
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