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	<title>№3 2024 &#8211; ВОПРОСЫ ЛЕСНОЙ НАУКИ/FOREST SCIENCE ISSUES</title>
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		<title>ELEMENTAL COMPOSITION OF SCOTS PINE WOOD, BARK AND NEEDLES IN THE MARI EL FORESTS</title>
		<link>https://jfsi.ru/en/7-3-2024-demakov_et_al/</link>
		
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					<description><![CDATA[         Yu. P. Demakov, O. V. Sheikina*, E. S. Sharapov           Volga State University of Technology, Lenina Square, 3, Yoshkar-Ola City, Republic of Mari El, 424000, Russia&#46;&#46;&#46;]]></description>
										<content:encoded><![CDATA[<p><a style="color: #000000;" href="http://jfsi.ru/wp-content/uploads/2024/12/7-3-2024-Demakov_et_al.pdf"><img loading="lazy" class="size-full wp-image-1122 alignright" src="http://jfsi.ru/wp-content/uploads/2018/10/pdf.png" alt="" width="32" height="32" /></a></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>         Yu. P. Demakov, O. V. Sheikina</strong><strong><sup>*</sup></strong><strong>, E. S. Sharapov</strong></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>          Volga State University of Technology,</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>Lenina Square, 3, Yoshkar-Ola City, Republic of Mari El, 424000, </em><em>Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong><sup>*</sup></strong>E-mail: ShejkinaOV@volgatech.net</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Received: 11.06.2023</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Revised: 15.09.2023</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Accepted: 25.09.2023</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The article presents the results of assessment of Scots pine (<em>Pinus sylvestris</em> L.) wood (216 pc), bark (29 pc), needle (127 pc) specimens for the content of 13 chemicals (Ca, K, Mg, Mn, Zn, Fe, Cu, Sr,Ni,Pb, Cr, Co, Cd), which were tested using an AAnalyst 400 atomic absorption spectrometer. The specimens were taken from the stands of different ages, origin and forest-growth conditions in the Republic of Mari El. It shows that the elemental composition of organ tissues of this tree species is its essential ecological and physiological characteristic that represents the peculiarities of the metabolism process in trees and a degree of tree adaptation to the environment. In comparison with the wood, the bark contains seven to eight times more calcium and strontium, four times more cadmium, two times more iron and zinc. As for the content of other elements, the bark does not differ much from the wood, however its ash content is 6.4 times greater. The ash content of the needles is 6.7 times greater than that of the wood, but the needles have a significantly higher concentration of К, Mn, Са, Zn, and in comparison with the bark a higher concentration of Sr, Ni, Pb. The contents of each chemical element in the tissues and organs of pine trees vary within wide ranges due to the environmental factors and individual features of trees. The variation of the Ni content in the wood is the greatest (СV = 92.1%), it is followed by Mg, Pb, Co and Fe (СV = 83%-89%). The Ca and ash contents in the wood vary the least (СV = 38 % and СV = 26.5%, respectively). The bark has the greatest variation of the Cd and Ni concentrations (СV = 172%), and they are followed by Sr, Mg, K (СV = 88%-111%). The Ca, Cu and ash contents in the bark vary the least (СV = 55%-62 %). The needles have the most significant variation in the Sr, Ni, Co contents (СV = 85%-96%) and the least variation in the K and ash contents (СV = 18%-24%). The contents of ash, Ca, Mg, Zn, K, Mn in the Scots pine wood, bark and needles as well as the ratios of К:Mn and Zn:Mn may be used for selection of economically valuable samples along with the other phenotypic characteristics of trees. It is cocluded that the ash composition of tree tissues, especially wood, is not suitable for biomonitoring purposes, since it largely depends on intracenotic factors, rather than technogenic pollution. For this purpose, it is better to evaluate the gross content of chemical elements in the litter and soil of biogeocenoses.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong><em>Keywords:</em></strong><em> the Republic of Mari El, Scots pine, wood, bark, needles, ash content, elemental composition, variation, causes</em></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span></p>
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<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span></p>
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		<title>TEMPERATURE REGIME OF LITTER IN DIFFERENT FOREST TYPES OF THE VALUEVSKY MOSCOW FOREST PARK</title>
		<link>https://jfsi.ru/en/7-3-2024-kuznetsova_et_al/</link>
		
		<dc:creator><![CDATA[lena]]></dc:creator>
		<pubDate>Mon, 09 Dec 2024 12:37:30 +0000</pubDate>
				<category><![CDATA[№3 2024]]></category>
		<guid isPermaLink="false">https://jfsi.ru/?p=6953</guid>

					<description><![CDATA[А. I. Kuznetsova1*, V. A. Kuznetsov2, E. V. Tikhonova1, D. N. Tebenkova1   1Centre for Forest Ecology and Productivity of the RAS Profsoyuznaya st. 84/32 bldg. 14, Moscow, 117997, Russia 2Lomonosov Moscow State University&#46;&#46;&#46;]]></description>
										<content:encoded><![CDATA[<p><a style="color: #000000;" href="https://jfsi.ru/wp-content/uploads/2025/01/7-3-2024-Kuznetsova_et_al.pdf"><img loading="lazy" class="alignright wp-image-1122 size-full" src="http://jfsi.ru/wp-content/uploads/2018/10/pdf.png" alt="" width="32" height="32" /></a></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>А</strong><strong>. I. Kuznetsova<sup>1*</sup>, V. A. Kuznetsov<sup>2</sup>, E. V. Tikhonova<sup>1</sup>, D. N. Tebenkova<sup>1</sup></strong></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em><sup>1</sup></em><em>Centre for Forest Ecology and Productivity of the RAS</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>Profsoyuznaya st. 84/32 bldg. 14, Moscow, 117997, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em><sup>2</sup></em><em>Lomonosov Moscow State University</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>Leninskiye Gori 1, Moscow, 119991, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">*E-mail: nasta472288813@yandex.ru</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Received: 11.08.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Revised: 15.09.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Accepted: 25.09.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The soil temperature regime is an important regulatory ecosystem function on which many biogeochemical processes depend. This article assesses the variation in the average monthly temperature of the surface organic soil horizon and litter stock in the Spruce-broadleaved and Lime-birch forest types of the Valuev Moscow Forest Park, taking into account intra- and interbiogeocenotic variability for 2019-2022. In all studied summer periods, the litter temperature of the oak-spruce forest is lower than that of the birch-linden forest. The variability of the litter temperature in winter depends on the depth of the snow cover, the onset of stable snow cover and litter reserves. A close negative relationship was found between the litter reserves and its temperature in summer, and a positive relationship in winter. In the presence of a thick snow cover, the litter temperature of the undercrown spaces is higher than the litter temperature of the window, which is characterized by low reserves. Further studies on the effect of woody vegetation on the characteristics of the soil surface temperature regime can be used to assess the rate of litter decomposition and greenhouse gas emission.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong><em> </em></strong></span><span style="font-family: 'times new roman', times, serif;"><strong><em>Keywords: </em></strong><em>quality of litter, mosaic elements, coniferous-broadleaf forests</em></span></p>
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<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Mahatkov I. D., Ermolov Ju. V., Osobennosti temperaturnogo rezhima lesnyh pochv severnoj tajgi Zapadnoj Sibiri (Spatial variation of the root zone layer temperature in the northern taiga of West Siberia), <em>Pochvy i okruzhayushchaya sreda, </em>2020, Vol<em>.</em> 2, No 4, pp. 1–11.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Orlova M. A., Lukina N. V., Smirnov V. Je., Metodicheskie podhody k otboru obrazcov lesnoj podstilki s uchetom mozaichnosti lesnyh biogeocenozov (Methodology of forest litter sampling taking into account the patchiness of forest biogeocoenoses), <em>Lesovedenie</em>, 2015, No 3, pp. 214–221.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Pristova T. A., Vlijanie drevesnoj rastitel&#8217;nosti na fizicheskie pokazateli snezhnogo pokrova srednej tajgi Respubliki Komi (Woody vegetation influence on snow cover (middle taiga of Komi Republic), <em>Forestry Bulletin</em>, 2024, Vol. 28, No 1, pp. 68–79, DOI: 10.18698/2542-1468-2024-1-68-79</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Tarasov P. A., Ivanov V. A., Ivanova G. A., Osobennosti temperaturnogo rezhima pochv v sosnjakah srednej tajgi, projdennyh nizovymi pozharami (Features of the temperature regime of soils in middle taiga pine forests subject to ground fires), <em>Hvojnye boreal&#8217;noj zony</em>, 2008, No 3-4, pp. 300–304.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Tihonova E. V., Tihonov G. N., Mozaichnost&#8217; fitocenozov hvojno-shirokolistvennyh lesov Valuevskogo lesoparka (Forest cover mosaics of coniferous-deciduous forests in the Valuevsky forest park), <em>Voprosy lesnoj nauki</em>, 2021, Vol. 4, No 3, pp. 52–87.</span></p>
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		<title>THE DEPENDENCE OF THE INDICATORS OF FLUCTUATING ASYMMETRY OF QUERCUS ROBUR L. LEAVES ON VARIOUS PARAMETERS OF THE CONDITION OF TREES IN CONDITIONS OF POLLUTION BY MOTOR VEHICLES</title>
		<link>https://jfsi.ru/en/7-3-2024-kulakova_kurganova/</link>
		
		<dc:creator><![CDATA[lena]]></dc:creator>
		<pubDate>Mon, 09 Dec 2024 12:22:06 +0000</pubDate>
				<category><![CDATA[№3 2024]]></category>
		<guid isPermaLink="false">https://jfsi.ru/?p=6943</guid>

					<description><![CDATA[          N. Yu. Kulakova1*, I. N. Kurganova2  1Institute of Forest Science RAS, Sovetskaya st. 21, Uspenskoe village, 143030 Moscow Region, Russia  2Institute of Physicochemical and Biological Problems of Soil Science&#46;&#46;&#46;]]></description>
										<content:encoded><![CDATA[<p><a style="color: #000000;" href="https://jfsi.ru/wp-content/uploads/2025/01/7-3-2024-Kulakova_Kurganova.pdf"><img loading="lazy" class="alignright wp-image-1122 size-full" src="http://jfsi.ru/wp-content/uploads/2018/10/pdf.png" alt="" width="32" height="32" /></a></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>          N. </strong></span><strong style="font-family: 'times new roman', times, serif;">Yu. Kulakova<sup>1*</sup>, I. N. Kurganova<sup>2</sup></strong></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span><span style="font-family: 'times new roman', times, serif;"><em><sup>1</sup></em><em>Institute of Forest Science RAS,</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>Sovetskaya st. 21, Uspenskoe village, 143030 Moscow Region, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span><span style="font-family: 'times new roman', times, serif;"><em><sup>2</sup></em><em>Institute of Physicochemical and Biological Problems of Soil Science RAS</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>FRC PSCBI RAS, Institutskaya st., bldg. 2, k. 2, 142290, Pushchino, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><sup>*</sup>E-mail: nkulakova@mail.ru</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Received: 14.08.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Revised: 14.09.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Accepted: 22.09.2024</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The relationships between the fluctuating asymmetry indices (FAI) of English oak leaves and the sanitary condition of trees, the concentration of Mg, P, K, Ca, Fe, Zn in leaves; Mg, P, K, Ca, Fe, Cu, Zn, Pb in branches and Na, Mg, P, K, Ca, Fe, Cu, Zn, Pb in the soil directly under the tree were studied. 28 trees located in places with different pollution levels (10–30 m from the Moscow Ring Road and Uzkoe forest park, Moscow) were examined. In the full sample of trees, significant positive correlations were found between the FAI of leaves and the concentration of Ca, Zn, S, Fe in them, as well as between the FAI of leaves and the concentration of Ca, Cu, Na, Fe, Zn in the soil. Negative dependencies were found between the FAI of leaves, the concentration of P in branches and the vital condition of trees. In the case of small samples (n = 10), the presence of correlations between the leaf PFA and the vital condition of trees was noted only in the group of trees in poor vital condition.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span><span style="font-family: 'times new roman', times, serif;"><strong><em>Keywords:</em></strong> <em>vehicle pollution, biodiagnostics, vital state of trees, powdery mildew, oak stands</em></span></p>
<p>&nbsp;</p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>REFERENCES</strong></span></p>
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		<title>AUTOMATIC SEGMENTATION OF TREE CROWNS IN PINE FORESTS  USING MASK R-CNN ON RGB IMAGERY FROM UAVS</title>
		<link>https://jfsi.ru/en/7-3-2024-nikitina-pdf/</link>
		
		<dc:creator><![CDATA[lena]]></dc:creator>
		<pubDate>Fri, 15 Nov 2024 09:04:23 +0000</pubDate>
				<category><![CDATA[№3 2024]]></category>
		<guid isPermaLink="false">https://jfsi.ru/?p=6897</guid>

					<description><![CDATA[Original Russian Text © 2024 A. D. Nikitina published in Forest Science Issues Vol. 7, No 2, Article 146.  © 2024                             &#46;&#46;&#46;]]></description>
										<content:encoded><![CDATA[<p><a style="color: #000000;" href="https://jfsi.ru/wp-content/uploads/2025/01/7-3-2024-Nikitina.pdf"><img loading="lazy" class="alignright wp-image-1122 size-full" src="http://jfsi.ru/wp-content/uploads/2018/10/pdf.png" alt="" width="32" height="32" /></a></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif; font-size: 10pt;">Original Russian Text © 2024 A. D. Nikitina published in Forest Science Issues Vol. 7, No 2, <a href="https://jfsi.ru/7-2-2024-nikitina/">Article 146</a>.<strong> </strong></span></p>
<p style="text-align: left;"><span style="font-family: 'times new roman', times, serif;"><strong>© 2024                                                                 </strong><strong>А</strong><strong>. D. Nikitina</strong></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>Center for Forest Ecology and Productivity of the RAS </em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em>Profsoyuznaya st. 84/32 bldg. 14, Moscow, 117997, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">E-mail: nikitina.al.dm@gmail.com</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Received: 18 May 2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Revised: 05 June 2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Accepted: 22 June 2024</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">This article presents the results of applying an improved method for automatic segmentation of RGB imagery (orthophotos) obtained using consumer-grade unmanned aerial vehicles (UAVs) based on the Mask R-CNN neural network. Preparation and post-processing blocks for raster and vector files were developed for geospatial data processing. The model was trained on 7,000 tree crowns identified in pine forest of drained habitats in the mixed coniferous-broadleaved forest subzone. Training was carried out using cross-validation. Additional data on 1,337 crowns were used for verification. Sequential filtering by area, score, and duplicate segments improved the quality of the final segmentation results for all age groups of pine forests. The model produced an average precision of 0.87, a recall of 0.81, and an F1-score of 0.83. The obtained results demonstrate the high efficiency of the filtering algorithm in reducing segment redundancy and increasing data reliability. The Mask R-CNN automatic segmentation method is an effective tool for studying the characteristics of pine forest stands based on RGB orthophotos obtained during UAV surveys; using this method, it is possible to reproduce the results of visual interpretation with high precision. This method is particularly effective for scaling studies to large areas, where manual interpretation would be labor-intensive.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Keywords:</strong><em> Mask R-CNN, automatic segmentation, tree detection, pine forest, RGB imagery, UAVs, environmental monitoring, remote sensing</em></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">In the context of global climate change, the issues of carbon balance and carbon stocks in forest ecosystems are becoming increasingly relevant. Effective monitoring of these parameters in forest ecosystems and forest resource management require obtaining detailed and accurate information about forest structure and condition (Espíndola, 2023). Within this context, the use of highly detailed GPS survey opens up new opportunities for environmental research and increases the efficiency of data collection and analysis. Forests with a predominance of Scotch pine (<em>Pinus sylvestris</em> L.) are common in the temperate latitudes of the Northern Hemisphere. This species is adaptable to diverse growing conditions and highly resistant to environmental stresses such as droughts and fires. Pine forests with their high ecological tolerance and significant contribution to the carbon cycle are an important object of environmental studies.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Existing studies (Medvedev et al., 2020; Tuominen et al., 2017; Nevalainen et al., 2017; Puliti et al., 2017; Ocer et al., 2020; Diez et al., 2021; Ball et al., 2023; Zhou et al., 2023) outline the prospects of UAV and neural network applications in image processing for accurate and efficient study of forests. However, there are relatively few studies on forests of complex structure with a closed canopy, hence the need for further studies and higher accuracy of methods used in these conditions. It is also essential to take into account the potential for use of mass-market UAVs, since their availability and widespread use make these methods applicable in applied and research practice for a wider range of users. The<em> purpose</em> of this study is to evaluate the effectiveness of the automatic segmentation method using the Mask R-CNN neural network to identify individual trees in pine forest of different structures based on RGB orthophotos obtained using UAVs. In this study, segmentation of &#8216;pine forests&#8217; primarily focuses on the upper canopy layer, where the crowns of pine trees form the dominant component.</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>MATERIALS AND METHODS</strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Objects of research.</strong> The objects of research are pine forests in the drained habitats of the coniferous-broadleaved forest subzone of the western part of the Russian Plain in the following protected areas: the <em>Kurshskaya Kosa</em> National Park (NP), the <em>Smolenskoye Poozerye</em> NP, the <em>Bryansky Les</em> State Natural Biosphere Reserve (SNBR). Three age groups were identified in the forests under study: young (10–40 years old), middle-aged (40–80 years old) and old (over 80 years old). Some studies (Nezami et al., 2020; Diez et al., 2021) show that segmentation algorithms demonstrate the highest learning efficiency on single-species and structurally simple forests. With the data obtained in the <em>Kurshskaya Kosa</em> NP, it is possible to better adjust the model, as the studied pine forests of this park mainly have a single-species composition with a 10C stand formula. In accordance with the Guide to Identifying Forest Types in the European Russia (http://cepl.rssi.ru/bio/forest/index.htm), the young pine forests fall into the group of xerophytic green-moss and green-moss-lichen pine forest types. Xerophytic green-moss pine forests are predominant in both middle-aged and old forests. Data obtained in the pine forests of the <em>Smolenskoye Poozerye</em> and <em>Bryansky Les</em> improve the quality of annotation for segmentation algorithms applied to forest stands of mixed composition and complex structure, making these algorithms more versatile. In the <em>Smolenskoye Poozerye</em> NP, the studied areas in middle-aged and old forests are dominated by low shrub-green-moss pine forests, whereas the young forests are mainly represented by small-grass-green-moss pine forests, with a closeness of 40–90%. Within the studied areas of the <em>Bryansky Les</em> Biosphere Reserve, middle-aged low shrub-green-moss pine forests and complex old pine forests with linden and oak are predominant, with a closeness of 70–80%.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Aerial survey using UAVs. </strong>In this study, the results of survey carried out using Phantom 3 Advanced and Mavic Pro UAVs by DJI were used. These devices are affordable and equipped with RGB cameras. Flight tasks were simulated using DroneDeploy software. The flights were performed at an altitude of 100–200 m depending on the complexity of the terrain and the height of the forest canopy with a longitudinal and transverse overlap of 90% with constant calm weather (wind velocity up to 10 m/s) at about 11:00 to 16:00 local time. The survey area using such parameters is ~15 hectares per battery.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Aerial images processing</strong> was carried out using Agisoft Metashape software and included the following main stages: uploading images; image alignment; building a dense point cloud; building a digital terrain model (DTM); building an orthophoto; rasterizing the DTMs and the orthophotos. The calculated spatial resolution of the DTMs varied from 15 to 32 cm/pixel depending on the altitude of the flight, whereas that of orthophotos was from 2 to 8 cm/pixel. The total number of initial images used to create orthophotos exceeded 20,000, with an average orthophoto resolution of 5.9 cm/pixel and DTM resolution of 23.6 cm/pixel. The total number of orthophotos was 55.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Visual interpretation. </strong>During interpretation, the boundaries of the crowns of individual trees were delineated manually using the QGIS software. Annotation is necessary to create training and validation datasets. It is carried out for the central sections of orthophotos ranging in size from 20×20 m (for young trees) to 100×100 m (for middle-aged and old forests). As a result, files with spatial vector data (.shp) with the crowns of individual trees in pine forest, as well as in additional key areas of diverse composition, were obtained to expand the training set during further segmentation. The final set of visual annotation data included ~8,300 individual crowns and covered 55 key sites. The most crowns were identified in pine forest — 6,799, including 3,330 in middle–aged forests, 2,325 in old forests, and 1,144 in young forests. Auxiliary areas with other species make up a smaller part (broadleaved forests — 562, spruce forests — 823, small-leaved forests — 141).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Automatic segmentation using the Mask R-CNN neural network. </strong>The ultra-precision Mask R-CNN neural network developed in 2017 (He et al., 2017) is used to identify individual tree crowns on aerial images. It expands the capabilities of the Faster R-CNN neural network due to the added module that predicts segmentation masks for regions of interest (RoI). This module works together with the classification and regression of the Bounding box. One of the features of Mask R-CNN is pixel-to-pixel alignment, which is not implemented in Fast/Faster R-CNN.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The following tools, frameworks and libraries were used to create the project: CUDA, Jupyter Notebook, QGIS, PyTorch, Rasterio, fiona, and Matplotlib. The study was carried out using the Mask R-CNN model in the Python PyTorch machine learning framework, pre-trained on the <em>COCO</em> dataset which includes more than 330,000 images and 1.5 million objects. The pre-trained model is able to identify the boundaries of objects in images. However, additional training is required for tree crown detection. This process is simpler and faster than learning from scratch, it reduces the risk of getting stuck in local minima and reduces the number of necessary adjustments. The neural network parameters were reconfigured for the classification of regions of interest, creation of bounding boxes, and mask segmentation.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em>Creating a dataset for model training. </em>The first step is to create a specialized dataset. The following source data were used for this task: UAV orthophotos (in GeoTIFF .tiff format); manually selected vector boundaries of tree crowns (in .shp format); boundaries of the areas under study (in .shp format). The model was trained on the contours of seven thousand tree crowns (84%) obtained during visual annotation from all the studied areas. The size of the validation set was 1,337 crowns (16%) from key sites of pine forests, stratified taking into account the object and the age of the stand.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Preparation stages for the data set included checking and adjustment of the vector file geometry (irregular shapes of objects, self-intersections, etc.), data reprojection; conversion of images to 24-bit format; ensuring the correct alignment of input data using uniform boundaries of the studied sites. The model accepts input images as a [W, H, 3] matrix (where W and H stand for width and height, respectively, and 3 is the number of RGB channels), therefore the original images were split into components of equal size based on the optimal grid. The width and height of each component were determined as the minimum among all images (Fig. 1).</span></p>
<p>(a)</p>
<p><img loading="lazy" class="size-large wp-image-6898" src="https://jfsi.ru/wp-content/uploads/2024/11/1а-1024x752.jpg" alt="" width="1024" height="752" srcset="https://jfsi.ru/wp-content/uploads/2024/11/1а-1024x752.jpg 1024w, https://jfsi.ru/wp-content/uploads/2024/11/1а-300x220.jpg 300w, https://jfsi.ru/wp-content/uploads/2024/11/1а-150x110.jpg 150w, https://jfsi.ru/wp-content/uploads/2024/11/1а-768x564.jpg 768w, https://jfsi.ru/wp-content/uploads/2024/11/1а.jpg 1188w" sizes="(max-width: 1024px) 100vw, 1024px" /><br />
(b)</p>
<div id="attachment_6899" style="width: 1034px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6899" loading="lazy" class="size-large wp-image-6899" src="https://jfsi.ru/wp-content/uploads/2024/11/1б-1024x785.jpg" alt="Figure 1. (a) A schematic diagram for splitting the source raster images into separate components, where W and H stand for width and height, respectively, and 3 is the number of RGB channels, and (b) individual components after splitting." width="1024" height="785" srcset="https://jfsi.ru/wp-content/uploads/2024/11/1б-1024x785.jpg 1024w, https://jfsi.ru/wp-content/uploads/2024/11/1б-300x230.jpg 300w, https://jfsi.ru/wp-content/uploads/2024/11/1б-150x115.jpg 150w, https://jfsi.ru/wp-content/uploads/2024/11/1б-768x589.jpg 768w, https://jfsi.ru/wp-content/uploads/2024/11/1б.jpg 1100w" sizes="(max-width: 1024px) 100vw, 1024px" /><p id="caption-attachment-6899" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 1. (a)</strong> A schematic diagram for splitting the source raster images</span><br /><span style="font-family: 'times new roman', times, serif;">into separate components, where W and H stand for width and height, respectively, and 3 is the number of RGB channels, and <strong>(b)</strong> individual components after splitting.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">A set of binary images of each segment (crown) where pixels have a value of [0] for the background and [1] for the crown was used for annotation (Fig. 2).</span></p>
<div id="attachment_6900" style="width: 1034px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6900" loading="lazy" class="size-large wp-image-6900" src="https://jfsi.ru/wp-content/uploads/2024/11/2-1024x334.png" alt="Figure 2. Converting an input dataset into a multidimensional array format." width="1024" height="334" srcset="https://jfsi.ru/wp-content/uploads/2024/11/2-1024x334.png 1024w, https://jfsi.ru/wp-content/uploads/2024/11/2-300x98.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/2-150x49.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/2-768x251.png 768w, https://jfsi.ru/wp-content/uploads/2024/11/2-1536x502.png 1536w, https://jfsi.ru/wp-content/uploads/2024/11/2-2048x669.png 2048w" sizes="(max-width: 1024px) 100vw, 1024px" /><p id="caption-attachment-6900" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 2.</strong> Converting an input dataset into a multidimensional array format.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Thus, files with visual annotation were transformed into multidimensional arrays, with each tree crown saved as a separate image. The final dataset accepted by the model included raster orthophotos (.png), information about the boundaries of the sites with the transformation configuration (.json), annotation masks in the form of rasters where each crown corresponds to a certain numerical pixel value (.png), and orthophotos cropped along the extended boundary for the correct identification of marginal objects (.png). Additionally, vector annotation data were loaded, which are not involved in training and are used at the stage of evaluation of the model performance.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em>Training of the Mask R-CNN neural network model. </em>To train the model, a prepared dataset was used, which was divided into training and validation subsets. Validation data were not used in the learning process. Repeated k-fold cross-validation was used for training data (k=10). The learning parameters of the neural network included the initial learning rate (LR), the LR schedule, the LR factor, the regularization coefficient, and the Stochastic Gradient Descent (SGD) parameter. The model was trained over 9 epochs, with the entire dataset passing through the neural network in each epoch, and the model weights adjusted. Transformations of the input image to enlarge the dataset included rotations as well as contrast, saturation, and brightness adjustments with a total probability of change 0.1. To prevent overfitting, the model was regularly evaluated using a validation dataset. Neural network functioning resulted in the creation of a multidimensional stack of monochrome images of each object with an indication of the confidence level ranging from 0 to 1. This indicator reflects the probability that the output object belongs to a given class (crown).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em>Processing of data obtained by the model. </em>To analyze the data of the trained neural network, orthophotos of various test areas in the .tiff format with the boundaries of key sites and the results of visual interpretation were transmitted for subsequent calculation of model quality metrics. Considering that the model works with images in pixel coordinates, an additional metadata file was created with information about the coordinate system, coordinates of the corners of the segmented area and the geographical reference.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Due to the limitation of the model to process no more than 100 segments (crowns) per image, it was necessary to divide the source raster into parts (patches) so that each of them had less than 100 crowns. However, when dividing images strictly according to the grid, distortions in segments at the boundaries of the sections are possible (Fig. 3).</span></p>
<p><span style="font-family: 'times new roman', times, serif;">a)<img loading="lazy" class="aligncenter size-large wp-image-6901" src="https://jfsi.ru/wp-content/uploads/2024/11/3а-1024x834.png" alt="" width="1024" height="834" srcset="https://jfsi.ru/wp-content/uploads/2024/11/3а-1024x834.png 1024w, https://jfsi.ru/wp-content/uploads/2024/11/3а-300x244.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/3а-150x122.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/3а-768x625.png 768w, https://jfsi.ru/wp-content/uploads/2024/11/3а.png 1600w" sizes="(max-width: 1024px) 100vw, 1024px" /></span></p>
<p><span style="font-family: 'times new roman', times, serif;"> b)</span></p>
<div id="attachment_6902" style="width: 780px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6902" loading="lazy" class="size-full wp-image-6902" src="https://jfsi.ru/wp-content/uploads/2024/11/3б.png" alt="Figure 3. An example of a) splitting an image into patches and b) a possible error in segmentation of marginal areas." width="770" height="608" srcset="https://jfsi.ru/wp-content/uploads/2024/11/3б.png 770w, https://jfsi.ru/wp-content/uploads/2024/11/3б-300x237.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/3б-150x118.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/3б-768x606.png 768w" sizes="(max-width: 770px) 100vw, 770px" /><p id="caption-attachment-6902" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 3.</strong> An example of a) splitting an image into patches and b) a possible error in segmentation of marginal areas.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The problem of marginal crowns which occurs when splitting an image in accordance with a grid was solved by creating a 50% overlap between patches and defining a zone of ignored boundaries to rule out edge effects. The offset information was saved to further restore the coordinates of the components in the original full-size image. The use of a pyramid of patches, where the size of components doubles at each level, provided adaptation to different scales of objects. The resulting segments were converted into images, and then into a vector format using the marching squares algorithm (confidence threshold = 0.5) implemented in the <em>Skimage</em> library. Crowns falling in the zone of ignored boundaries were removed from the results, thus reducing the number of duplicated and marginal crowns. The remaining segments were combined into a single dataset, where the score was indicated for each identified crown.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em>Filtering of the segmentation data. </em>Filtering in the context of neural network data processing is an important step aimed at improving the quality of results. During the splitting of images into separate components, a large overlap is assumed, which prevents the model from missing the marginal crowns of trees; however, when assembling the segmentation results into one dataset, duplicates of the same crown are created. In addition to possible duplicates, there may be objects with an irregular shape, unreliable area, or with a low confidence level. All this requires careful filtering which includes the analysis of various parameters in order to determine the optimal criteria for removing unwanted segments.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Optimal parameters for the filtering algorithm were calculated based on data with the calculated Intersection over Union (IoU) metric, which measures the degree of intersection between the crowns predicted by the neural network and the crowns identified visually. These data consisted of a set of points, where each point corresponded to a detected crown with several parameters (area, score, IoU). During the scatter plot analysis (Fig. 4), the threshold for filtering segments with a small area is clearly seen. This filtering step significantly reduced the number of excessively segmented crowns (28%) without significant loss of precision. The scatter plot also shows that the majority of segments with the minimal IoU values also have a low score, so it is advisable to use the score as a filtering parameter in the future.</span></p>
<div id="attachment_6905" style="width: 899px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6905" loading="lazy" class="wp-image-6905 size-full" src="https://jfsi.ru/wp-content/uploads/2024/11/4.png" alt="Figure 4. A scatter plot showing the relationship between the area of a segment (√S, pixels), its score, and the degree of intersection of the segment predicted by the neural network with the reference segment of the annotation (IoU)." width="889" height="630" srcset="https://jfsi.ru/wp-content/uploads/2024/11/4.png 889w, https://jfsi.ru/wp-content/uploads/2024/11/4-300x213.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/4-150x106.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/4-768x544.png 768w" sizes="(max-width: 889px) 100vw, 889px" /><p id="caption-attachment-6905" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 4.</strong> A scatter plot showing the relationship between the area of a segment (√S, pixels), its score, and the degree of intersection of the segment predicted by the neural network with the reference segment of the annotation (IoU).</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">To remove duplicate crowns, filtering was used based on the degree of intersection and reliability of the data. If there is a significant overlap between two crowns, the one with a higher score of the neural network is selected. If there is one large and multiple small overlapping segments, only the large one remains if its score is higher. If its score is lower, such a segment is excluded. Therefore, if there is high confidence in smaller segments, a large crown is discarded (Fig. 5a), and vice versa (Fig. 5b). Removing duplicates also contributed to a significantly higher precision.</span></p>
<div id="attachment_6906" style="width: 1034px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6906" loading="lazy" class="size-large wp-image-6906" src="https://jfsi.ru/wp-content/uploads/2024/11/5-1024x408.png" alt="Figure 5. Filtering options for overlapping crowns with different confidence levels (green segments are saved in the final list, whereas red ones are removed)." width="1024" height="408" srcset="https://jfsi.ru/wp-content/uploads/2024/11/5-1024x408.png 1024w, https://jfsi.ru/wp-content/uploads/2024/11/5-300x119.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/5-150x60.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/5-768x306.png 768w, https://jfsi.ru/wp-content/uploads/2024/11/5.png 1382w" sizes="(max-width: 1024px) 100vw, 1024px" /><p id="caption-attachment-6906" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 5.</strong> Filtering options for overlapping crowns with different confidence levels (green segments are saved in the final list, whereas red ones are removed).</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The developed sequential filtering included criteria for area and score, and then for segment duplicates. This made it possible to preserve high-quality segments, minimizing loss in recall.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em>Creation of the final vector layer. </em>To transform the coordinates of the segments into geographical ones and create the final vector file in the .shp format, a metadata file created during the data processing stage was used. Figure 6 shows the neural network&#8217;s crown segmentation results, demonstrating the precision of coordinate transformation.</span></p>
<div id="attachment_6907" style="width: 1034px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6907" loading="lazy" class="size-large wp-image-6907" src="https://jfsi.ru/wp-content/uploads/2024/11/6-1024x862.png" alt="Figure 6. An example of a sample site, where (a) is an orthophoto without annotation, (b) is visual interpretation, (c) is the result of automatic segmentation without filtering, and (d) is the result of automatic segmentation after filtering." width="1024" height="862" srcset="https://jfsi.ru/wp-content/uploads/2024/11/6-1024x862.png 1024w, https://jfsi.ru/wp-content/uploads/2024/11/6-300x252.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/6-150x126.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/6-768x646.png 768w, https://jfsi.ru/wp-content/uploads/2024/11/6.png 1243w" sizes="(max-width: 1024px) 100vw, 1024px" /><p id="caption-attachment-6907" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 6.</strong> An example of a sample site, where (a) is an orthophoto without annotation, (b) is visual interpretation, (c) is the result of automatic segmentation without filtering, and (d) is the result of automatic segmentation after filtering.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The diagram (Fig. 7) shows the final data processing process for the segmentation of pine tree crowns using the Mask R-CNN algorithm. The upper part of the diagram reflects the research stages, including the creation of a training dataset, actual training of the Mask R-CNN model and selection of the filtering parameters. These steps are performed once to set up the model. The lower part of the diagram demonstrates the processing stage. It begins with uploading raster files, and then the input data is prepared, followed by segment selection and filtering of the results. As a result, a vector file is created that can be used for further analysis.</span></p>
<div id="attachment_6908" style="width: 1034px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6908" loading="lazy" class="size-large wp-image-6908" src="https://jfsi.ru/wp-content/uploads/2024/11/7-1024x414.png" alt="Figure 7. Data processing steps for automatic crown detection." width="1024" height="414" srcset="https://jfsi.ru/wp-content/uploads/2024/11/7-1024x414.png 1024w, https://jfsi.ru/wp-content/uploads/2024/11/7-300x121.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/7-150x61.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/7-768x310.png 768w, https://jfsi.ru/wp-content/uploads/2024/11/7-1536x621.png 1536w, https://jfsi.ru/wp-content/uploads/2024/11/7-2048x828.png 2048w" sizes="(max-width: 1024px) 100vw, 1024px" /><p id="caption-attachment-6908" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 7.</strong> Data processing steps for automatic crown detection.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em>Model quality metrics. </em>To evaluate the precision of the neural network in recognizing tree crowns, the results of visual interpretation of orthophotos were used. The crown was considered to be detected correctly if the IoU exceeded 0.5, which is the standard value found in studies on segmentation (Aubry-Kientz et al., 2019; Hao et al., 2021; Ball et al., 2023). For the model quality evaluation, standard error matrices were calculated: TP (true positive) — correct determination of a crown; FP (false positive) — incorrect determination of an object as a crown; FN (false negative) — incorrect exclusion of a crown; TN (true negative) — equal to 0 in segmentation tasks. Based on these data, key metrics were calculated as follows: precision — the proportion of correctly identified crowns among all recognized ones; recall — the proportion of correctly identified crowns from all actually existing ones; F1-score — the harmonic mean between precision and recall, which ensures a balance of these parameters.</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>RESULTS AND DISCUSSION</strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">At all key sites, the initial results of neural network segmentation had high recall (0.91 for all sites) values and low precision (0.31) and F1-score (0.46) values; segment redundancy can also be seen in the ratio of the number of segmented crowns to visual detection data. Filtering significantly improved the final average precision (0.87) and F1-score (0.83), while the final recall slightly decreased (recall = 0.81).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The chart (Fig. 8) reflecting the change in the F1-score at different filtering stages for different age groups of pine forest shows that after all filtering stages, the median values of the F1-score increase for all age groups, which is evidence of improved quality of segmentation for the entire sample. However, the improvement after filtering is most pronounced for old pine forests (over 80 years old). This is indicatory of the effectiveness of the applied filtering approach to improve the quality of segmentation results, reducing redundancy and increasing data reliability.</span></p>
<div id="attachment_6909" style="width: 1034px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6909" loading="lazy" class="size-large wp-image-6909" src="https://jfsi.ru/wp-content/uploads/2024/11/8-1024x620.png" alt="Figure 8. Changes in F1-score at different filtering stages for pine forests of different age groups." width="1024" height="620" srcset="https://jfsi.ru/wp-content/uploads/2024/11/8-1024x620.png 1024w, https://jfsi.ru/wp-content/uploads/2024/11/8-300x182.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/8-150x91.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/8-768x465.png 768w, https://jfsi.ru/wp-content/uploads/2024/11/8.png 1314w" sizes="(max-width: 1024px) 100vw, 1024px" /><p id="caption-attachment-6909" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 8.</strong> Changes in F1-score at different filtering stages for pine forests of different age groups.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The analysis of the training and validation samples used to control overfitting when setting up the model showed the greatest differences in the group of young pine forests (F1<sub>training</sub> = 0.81, F1<sub>validation</sub> = 0.70) with a median value of 0.8 for all key sites. Middle-aged and old pine forest have high F1-scores for both the training (0.84 and 0.88, respectively) and validation sets (0.83 and 0.82, respectively) of the sites, with a median F1-score of 0.88 for both groups.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The spread of model quality values in pine forests was 0.53–0.96 with an average value of 0.83 and a median value of 0.85. In young forests, the spread of results (F1 = 0.53–0.89) shows lower adaptability of the model to some stands of this age, whereas the results are high on average (F1<sub>average</sub> = 0.77, F1<sub>median </sub>= 0.8). This may be due to the low quality of the survey (for low stands, it would make sense to carry out UAV surveys at an altitude below 120–180 m when using mass-market UAVs), difficulties with detecting individual trees in dense stands, and a smaller training sample for sample sites with young pine forests. The results were more stable (F1 = 0.7–0.96) for old forests with an average value of F1 = 0.86 (F1<sub>median</sub> = 0.88).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The study showed that the adapted Mask R-CNN model provides high precision of results in different age groups of pine forest with different values of closeness, since the indicators of segmentation quality in key sites remain high for all datasets. An example of segmentation results is shown in Figure 9.</span></p>
<p>a)</p>
<p><img loading="lazy" class="aligncenter size-full wp-image-6910" src="https://jfsi.ru/wp-content/uploads/2024/11/9a.png" alt="" width="830" height="537" srcset="https://jfsi.ru/wp-content/uploads/2024/11/9a.png 830w, https://jfsi.ru/wp-content/uploads/2024/11/9a-300x194.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/9a-150x97.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/9a-768x497.png 768w" sizes="(max-width: 830px) 100vw, 830px" /></p>
<p>b)</p>
<p><img loading="lazy" class="aligncenter size-full wp-image-6911" src="https://jfsi.ru/wp-content/uploads/2024/11/9b.png" alt="" width="830" height="530" srcset="https://jfsi.ru/wp-content/uploads/2024/11/9b.png 830w, https://jfsi.ru/wp-content/uploads/2024/11/9b-300x192.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/9b-150x96.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/9b-768x490.png 768w" sizes="(max-width: 830px) 100vw, 830px" /></p>
<p>c)</p>
<div id="attachment_6912" style="width: 834px" class="wp-caption aligncenter"><img aria-describedby="caption-attachment-6912" loading="lazy" class="size-full wp-image-6912" src="https://jfsi.ru/wp-content/uploads/2024/11/9c.png" alt="Figure 9. An example of a key site where (a) is visual interpretation, (b) is the result of segmentation without filtering, and (c) is the result of segmentation after filtering." width="824" height="534" srcset="https://jfsi.ru/wp-content/uploads/2024/11/9c.png 824w, https://jfsi.ru/wp-content/uploads/2024/11/9c-300x194.png 300w, https://jfsi.ru/wp-content/uploads/2024/11/9c-150x97.png 150w, https://jfsi.ru/wp-content/uploads/2024/11/9c-768x498.png 768w" sizes="(max-width: 824px) 100vw, 824px" /><p id="caption-attachment-6912" class="wp-caption-text"><span style="font-family: 'times new roman', times, serif;"><strong>Figure 9.</strong> An example of a key site where (a) is visual interpretation, (b) is the result of segmentation without filtering, and (c) is the result of segmentation after filtering.</span></p></div>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">In studies on segmentation of individual trees in stands, closeness of the stands under study is an important factor. N. E. Ocer et al. (2020) carried out a study on detection of individual trees using the Mask R-CNN and Feature Pyramid Nets (FPNs) and obtained F1-scores within 0.82–0.91 for three test images. Sparse stands were analyzed in the study by N. V. Ivanova et al. (Ivanova et al., 2021), where watershed and region growing methods were applied and F1-scores of 0.7–0.9 were obtained. More closed stands are considered in the paper by X. Chen et al. (2023), with F1-scores between 0.71 and 0.79. The study by M. Beloiu et al. (2023) is focused on closed and diverse species stands with F1-scores ranging from 0.44 to 0.92. Studies show that the effectiveness of crown segmentation depends on the closeness of stands, and with its increase, the precision of segmentation becomes more variable.</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>CONCLUSIONS</strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The method of automatic image segmentation using the Mask R-CNN neural network is an effective tool for research of pine forest that can reproduce the results of visual interpretation with high precision. The splitting of RGB orthophotos made it possible to take into account individual tree crowns in a closed canopy to the fullest extent possible. The initial results had high recall values; however, a result filtering unit was developed to increase precision. Filtering made it possible to eliminate redundant segments and improve the precision of the results, while maintaining a high degree of crown recognition. For all age groups of pine forests, there was an increase in F1-score after filtering. The final model demonstrates consistently high segmentation quality (F1-score = 0.83) of pine forest.</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>FINANCING</strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">The work was carried out with support from the Laboratory of Forest Climate-regulating Functions (project 122111500023-6) of the Center for Forest Ecology and Productivity of the RAS (CEPF RAS).</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>REFERENCES</strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Agisoft Metashape, available at: <a href="http://www.agisoft.com">http://www.agisoft.com</a> (2024, 01 June).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Aubry-Kientz M., Dutrieux R., Ferraz A., Saatchi S., Hamraz H., Williams J., A comparative assessment of the performance of individual tree crowns delineation algorithms from ALS data in tropical forests, <em>Remote Sensing</em>, 2019, Vol. 11, No 9, pp. 1086 (1–21).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Ball J. G., Hickman S. H., Jackson T. D., Koay X. J., Hirst J., Jay W., Coomes D. A., Accurate delineation of individual tree crowns in tropical forests from aerial RGB imagery using Mask R-CNN, <em>Remote Sensing in Ecology and Conservation</em>, 2023, Vol. 9, No 5, pp. 641–655.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Beloiu M., Heinzmann L., Rehush N., Gessler A., Griess V. C., Individual Tree-Crown Detection and Species Identification in Heterogeneous Forests Using Aerial RGB Imagery and Deep Learning, <em>Remote Sensing</em>, 2023, Vol. 15, p. 1463.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Chen X., Shen X., Cao L., Tree Species Classification in Subtropical Natural Forests Using High-Resolution UAV RGB and SuperView-1 Multispectral Imageries Based on Deep Learning Network Approaches: A Case Study within the Baima Snow Mountain National Nature Reserve, China, <em>Remote Sensing</em>, 2023, Vol. 15, p. 2697.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Diez Y., Kentsch S., Fukuda M., Caceres M. L. L., Moritake K., Cabezas M., Deep Learning in Forestry Using UAV-Acquired RGB Data: A Practical Review, <em>Remote Sens.</em>, 2021, Vol. 13, p. 2837.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Espíndola R. P., Ebecken N. F. F., Advances in remote sensing for sustainable forest management: monitoring and protecting natural resources, <em>Revista Caribeña de Ciencias Sociales</em>, 2023, Vol. 12, No 4, pp. 1605–1617.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Hao Z., Lin L., Post C.J., Mikhailova E.A., Li M., Chen Y. et al., Automated tree-crown and height detection in a young forest plantation using mask region-based convolutional neural network (Mask R-CNN), <em>ISPRS Journal of Photogrammetry and Remote Sensing</em>, 2021, Vol. 178, pp. 112–123.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">He K., Gkioxari G., Dollár P., Girshick R., Mask R-CNN, <em>Proceedings of the IEEE International Conference on Computer Vision</em>, 2017, pp. 2961–2969.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">https://cepl.rssi.ru/bio/forest/index.htm (2024, 1 June).</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Ivanova N. V., Shashkov M. P., Shanin V. N., Study of pine forest stand structure in the priosko-terrasny state nature biosphere reserve (Russia) based on aerial photography by quadrocopter, <em>Nature Conservation Research</em>, 2021, Vol. 6, No 4, pp. 1–14.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Medvedev A. A., Tel&#8217;nova N. O., Kudikov A. V., Alekseenko N. A., Analiz i kartografirovanie strukturnyh parametrov redkostojnyh severotajozhnyh lesov na osnove fotogrammetricheskih oblakov tochek (Use of photogrammetric point clouds for the analysis and mapping of structural variables in sparse northern boreal forests), <em>Sovremennye problemy distancionnogo zondirovanija Zemli iz kosmosa</em>, 2020, Vol. 17, No 1, pp. 150–163.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Nevalainen O., Honkavaara E., Tuominen S., Viljanen N., Hakala T., Yu X., Hyyppä J., Saari H., Pölönen I., Imai N. N., Tommaselli A. M. G., Individual tree detection and classification with UAV-based photogrammetric point clouds and hyperspectral imaging, <em>Remote Sensing</em>, 2017, Vol. 9, No 3, p. 185.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Nezami S., Khoramshahi E., Nevalainen O., Pölönen I., Honkavaara E., Tree species classification of drone hyperspectral and RGB imagery with deep learning convolutional neural networks, <em>Remote Sensing</em>, 2020, Vol. 12, No. 7, p. 1070.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Ocer N. E., Kaplan G., Erdem F., Matci D.K., Avdan U., Tree extraction from multi-scale UAV images using Mask R-CNN with FPN, <em>Remote Sensing</em>, 2020, Vol. 11, p. 847–856.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Puliti S., Ene L. T., Gobakken T., Næsset E., Use of partial-coverage UAV data in sampling for large scale forest inventories, <em>Remote Sensing of Environment</em>, 2017, Vol. 194, pp. 115–126.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Tuominen S., Näsi R., Honkavaara E., Balazs A., Hakala T., Viljanen N., Reinikainen J., Tree species recognition in species rich area using UAV-borne hyperspectral imagery and stereo-photogrammetric point cloud, <em>International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences</em>, 2017, Vol. XLII-3/W3, pp. 185–194.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Zhou J., Chen X., Li S., Dong R., Wang X., Zhang C., Zhang L., Multispecies individual tree crown extraction and classification based on BlendMask and high-resolution UAV images, <em>Journal of Applied Remote Sensing</em>, 2023, Vol. 17, No 1, p. 016503.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong>Reviewed by:</strong> Candidate of Geographical Sciences N. V. Malysheva</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong><em> </em></strong></span></p>
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		<title>SCIENTIFIC HERITAGE OF PROFESSOR O. V. SMIRNOVA IN FOREST ECOLOGY  (TO THE 85TH ANNIVERSARY)</title>
		<link>https://jfsi.ru/en/7-3-2024-evstigneev/</link>
		
		<dc:creator><![CDATA[lena]]></dc:creator>
		<pubDate>Tue, 08 Oct 2024 07:56:45 +0000</pubDate>
				<category><![CDATA[№3 2024]]></category>
		<guid isPermaLink="false">https://jfsi.ru/?p=6781</guid>

					<description><![CDATA[     O. I. Evstigneev1,2   1State Nature Biosphere Reserve &#8220;Bryanskii Les&#8221;, Nerussa Station, Bryansk Oblast, 242180, Russia  2Center for Forest Ecology and Productivity of the RAS, Profsoyuznaya st. 84/32 bldg. 14, Moscow, 117997,&#46;&#46;&#46;]]></description>
										<content:encoded><![CDATA[<p><a style="color: #000000;" href="https://jfsi.ru/wp-content/uploads/2025/01/7-3-2024-Evstigneev.pdf"><img loading="lazy" class="alignright wp-image-1122 size-full" src="http://jfsi.ru/wp-content/uploads/2018/10/pdf.png" alt="" width="32" height="32" /></a></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>     O. </strong></span><strong style="font-family: 'times new roman', times, serif;">I. Evstigneev<sup>1,2</sup></strong></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong> </strong></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em><sup>1</sup></em><em>State Nature Biosphere Reserve &#8220;Bryanskii Les&#8221;, Nerussa Station, Bryansk Oblast, 242180, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><em> </em></span><span style="font-family: 'times new roman', times, serif;"><em><sup>2</sup></em><em>Center for Forest Ecology and Productivity of the RAS, Profsoyuznaya st. 84/32 bldg. 14, Moscow, 117997, Russia</em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">E-mail: quercus_eo@mail.ru</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Received: 16.08.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Revised: 24.09.2024</span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;">Accepted: 27.09.2024</span></p>
<p><span style="font-family: 'times new roman', times, serif;">O. V. Smirnova is a professor, doctor of biological sciences, and a leading scientist in the field of plant demography, population biology, and forest biogeocenology. O. V.Smirnova’s biogeocenotic views are based on ideas about the population organization of living cover, which were formed under the influence of her teacher, prof. A. A. Uranov. Within the framework of this system of views, O. V. Smirnova made a significant contribution to the development of concepts of the biological age of plants and the population strategy of plants, to the creation of the theory of coenopopulations and the population organization of biogeocenoses, as well as to the formation of ideas about modern zonality as an anthropogenic phenomenon. The article provides a complete bibliography of O. V. Smirnova’s papers, including the titles of her PhD students’ dissertations.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;"><strong><em>Keywords:</em></strong><em> biological age of plants, coenopopulation, forest biogeocenology, forest ecology, historical ecology, modern zonality, population strategy of plants </em></span></p>
<p style="text-align: center;"><span style="font-family: 'times new roman', times, serif;"><strong>REFERENCES</strong></span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Grime J. P., <em>Plant strategies and vegetation processes</em>, N.Y., 1979, 222 p.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Korotkov V. N., Novaja paradigma v lesnoj jekologii (New paradigm in forest ecology), <em>Biologicheskie nauki,</em> 1991, No 8, pp. 7–20.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Rabotnov T. A., Zhiznennyj cikl mnogoletnih travjanistyh rastenij v lugovyh ceno-zah (Life cycle of perennial herbaceous plants in meadow cenoses), <em>Geobotanika</em>, 1950, No 6, pp. 7–204.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Ramenskij L. G., O principial&#8217;nyh ustanovkah, osnovnyh ponjatijah i terminah pro-izvodstvennoj tipologii zemel&#8217;, geobotaniki i jekologii (On the fundamental principles, basic concepts and terms of industrial typology of lands, geobotany and ecology), <em>Sovetskaja botanika</em>, 1935, No 4, pp. 25–41.</span></p>
<p style="text-align: justify;"><span style="font-family: 'times new roman', times, serif;">Zaugol&#8217;nova L. B., Struktura populyacij semennyh rastenij i problemy ih monito-ringa (Structure of seed plant populations and problems of their monitoring), Avtoref. dis. … dok. biol. nauk v forme nauchnogo doklada, SPb, St Petersburg University, 1994, 70 p.</span></p>
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