WO2023282787A1 - Method of generating soil degradation maps - Google Patents
Method of generating soil degradation maps Download PDFInfo
- Publication number
- WO2023282787A1 WO2023282787A1 PCT/RU2021/000530 RU2021000530W WO2023282787A1 WO 2023282787 A1 WO2023282787 A1 WO 2023282787A1 RU 2021000530 W RU2021000530 W RU 2021000530W WO 2023282787 A1 WO2023282787 A1 WO 2023282787A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- degradation
- soil
- maps
- values
- binary
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
Links
Classifications
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01C—MEASURING DISTANCES, LEVELS OR BEARINGS; SURVEYING; NAVIGATION; GYROSCOPIC INSTRUMENTS; PHOTOGRAMMETRY OR VIDEOGRAMMETRY
- G01C11/00—Photogrammetry or videogrammetry, e.g. stereogrammetry; Photographic surveying
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
- G01N33/24—Earth materials
-
- G—PHYSICS
- G06—COMPUTING OR CALCULATING; COUNTING
- G06F—ELECTRIC DIGITAL DATA PROCESSING
- G06F18/00—Pattern recognition
Definitions
- the technical solution claimed as an invention relates to the field of agriculture, namely to precise precision coordinate farming, and is intended for the use of deep machine learning (neural networks) in the selection of satellite images over a long period in order to create soil degradation maps that reflect degradation areas within agricultural fields.
- Satellite images help to obtain dynamic information about agricultural land and respond in time to emerging deviations.
- space monitoring technologies has expanded the possibilities of operational tracking of the state of agricultural land.
- the use of satellite information data makes it possible to increase the accuracy of measuring biometric indicators of fields, which, using neural networks, makes it possible to interpolate the values of these indicators over a long period, and in the shortest possible time.
- the task of obtaining an integral characteristic of soil changes over decades is relevant.
- the integral characteristics are the values of the coefficients of the multitemporal line of soils. Reconciliation of computational data with empirical data obtained as a result of inspecting a particular field on the spot makes it possible to avoid obtaining unspecified information as much as possible.
- Degradation can be predicted by modeling degradation processes and obtaining terrain characteristics from topographic maps and digital elevation models. Degradation sites predicted by modeling require further confirmation, as degradation may or may not occur under the same topography and climate. Degradation can be detected based on the analysis of a large number of satellite images in the manual interpretation mode. In this case, the accuracy of detection and determination of the boundaries of degraded territories is higher than in land-based surveys.
- the main disadvantages of manual interpretation of a large number of satellite images include the high cost of highly skilled human labor, which cannot be automated, and low productivity.
- Modern trends in automating the identification and mapping of areas of soil degradation are based on the analysis of vegetation indices of vegetation, the analysis of which causes problems if they are carried out in the automatic mode of selecting images suitable for calculations.
- cloud masks are found in archives of satellite images, but usually these masks are not enough to diagnose the presence or absence of clouds on satellite images, and including even one unsuitable image in the processing of multi-time satellite imagery completely distorts the calculation results.
- the current trend in selecting satellite images is based on the use of deep machine learning, which allows you to select the necessary satellite images.
- Pattern recognition is one of the most demanded tasks of artificial intelligence and can be used in a wide variety of application areas. Neural networks are currently used most widely for pattern recognition. In some cases, they show results comparable or superior to human capabilities in solving similar problems. But in a number of cases, the expansion of their use is hindered by the difficulty of interpreting the resulting solution. Indeed, for a number of the most critical applications, verification and human approval/rejection of the automatic solution is required or naturally expected.
- CNN convolutional neural networks
- a prior analogue of the claimed technical solution is known, a method for remotely determining the state and use of agricultural land according to the Russian application for invention N ° 2018111761 of 04/02/2018, IPC: G01 W 1/00, G01W 1/08 published on 04.10.2019
- the analog describes an information management tool and an automated system for monitoring agricultural land, which use unmanned aerial vehicles of an aircraft type with multispectral cameras placed on them, as well as ground equipment in the form of a multispectral camera and a thermal imager installed on a mobile tower on the ground, allowing to produce advance survey and allocate areas for detailed studies of areas of degraded land subject to water and wind erosion and waterlogging.
- This analogue characterizes the previous generation of methods for diagnosing soil with spectral survey and collection of thematic cartographic materials using aircraft.
- This analogue according to the Russian application for the invention Ne 2018111761 does not provide for the analysis of multi-time series of satellite imagery using neural networks.
- An analogue of a new generation is known, a method for pre-harvest desiccation of crops with a variable rate within one field according to the Russian patent for the invention M? equipment using satellite navigation for individual analysis of intra-field zones, previously designed on the cartographic contour of the field, and calculation of the dosage of the drug applied to improve the parameters of the field sown with crops, and for a single field, a task map previously developed by an agronomist based on the values of the vegetation index NDVI and based on the determination of the norm of the working solution during visual inspection, the fields are loaded into the on-board computer installed in the sprayer cabin, then using the on-board computer, geolocation is established using the GPS / GLONASS system, and the on-board computer in the process e sprayer operation reads the norms from the task card at a specific point in the field and in in the process of desiccation, adjusts the rate of consumption of the working solution of the drug in each section of the field according to the loaded map-task during desic
- the technical solution of the RF patent DO°2717933 has signs of similarity with the claimed technical solution, such as the creation of maps of the field inhomogeneity of the field using satellite information.
- the relatively narrow range of application reduces the effectiveness of the prototype method, while in the claimed solution, satellite imagery is selected over a multi-year period.
- the similarity is the study of the NDVI vegetation index, however, in the prototype, this index is calculated once, according to the analysis of one frame of a satellite imagery, and in the claimed technical solution, the NDVI index is calculated for each field for each image for a period of time since 1984.
- the frequency of occurrence of low NDVI in the proposed solution shows areas not with random, but with persistent annual problems in the development of plants, respectively, the ability to determine the location of soil degradation with the greatest accuracy is achieved.
- the purpose of the proposed technical solution is based on the processing of multi-temporal satellite images to achieve the possibility of mapping areas of soil degradation within agricultural fields.
- the technical task is to create a reliable and as close as possible to reality cartographic representation of the results of the analysis of multi-temporal satellite images, for which the claimed method has been developed.
- degraded areas of arable land were indicated based on the selection of satellite images using deep machine learning methods and methods for calculating the average occurrence of low values of the vegetation index NDVI.
- EFFECT expanding the operational capabilities of mapping and automating the process of recognizing degraded soil cover areas inside agricultural fields using in practice the optimal parameters of the method for creating maps of soil cover degradation based on the results of processing multi-time satellite images.
- the operation of the training unit of the neural network recognition path which provides the final classification solution for the studied field maps, increases the probability of correct classification of satellite information, and subsequent verification on the field allows to maximize the accuracy of the resulting maps. The achievement of this result is ensured by the features of the proposed method.
- the method of generating maps of soil degradation based on the processing of multi-temporal satellite images includes the creation of maps of soil cover degradation using satellite information, in which Landsat satellite images are downloaded for each studied point on the Earth's surface from different frames of satellite imagery for many years, then with the help of a trained neural network, images are selected that do not have defects that prevent the calculation of vegetation indices, the vegetation index NDVI is calculated for each suitable image, the average occurrence of low NDVI values (AOLNDVI ), make a binary map of the development of soil cover degradation within the agricultural field and conduct empirical field measurements of the thickness of the humus horizon to verify the results obtained.
- AOLNDVI average occurrence of low NDVI values
- the claimed method consistently applies the principles of binary logic and measurement of the frequency of occurrence of a binary attribute (low NDVI value) in a large number of satellite images.
- the manifestation of a binary feature of each specific satellite image is not an independent characteristic in this approach.
- low NDVI values in any particular year can be associated with soil degradation factors, weather fluctuations, deficiencies in agricultural technologies, properties of a particular crop, etc.
- Figure 1 Suitable and not suitable for calculating vegetation indices, images sorted by a neural network, where: 1 - suitable for calculations; 2 - not suitable due to cloudiness; 3 - unusable due to cloud shadows; 4 - parts of crops not suitable due to wetting; 5 - unsuitable due to the lack of crop vegetation; 6 - unsuitable due to snow cover; 7 - unsuitable due to coverage with crop residues; 8 - not suitable due to the presence of combustion and combustion products; 9 - 14 - not suitable due to the presence of errors in agricultural technology.
- Fig.2 Stages of calculating soil degradation maps, where: 1 - calculation of NDV1 maps for each field and each Landsat scene, selected by the neural network; 2 - highlighting the area of low NDV1 values for each NDVI map (one third of the map area); 3 - calculation of the map of the average occurrence of low NDVI values; 4 - construction of a binary map of the distribution of soil degradation, where more than 50% of the times in 35 years low NDVI values were encountered.
- Fig.3 Binary map of soil degradation, built on the basis of processing multi-temporal satellite images selected by the neural network, and the points of field measurements of the thickness of the humus horizon to verify the results obtained (the numbers indicate the points of field measurements, the results of processing, which presented in the table). Green - areas with a predicted absence of degradation, red - areas of potential degradation of the soil cover.
- Fig.4 Traditional soil map and locations of field measurements (the numbers indicate the points of field measurements, the results of processing, which are presented in the table).
- the numbers in circles on a traditional soil map mean: 2 - no degradation, 3 - weak wind degradation, 4 - weak water degradation, 6 - medium water degradation, 7 - strong water degradation, 9 - soils of another type.
- soil degradation zones were calculated based on the frequency of occurrence of low NDVI values from 1984 to 2021.
- Low NDVI values were calculated separately for each suitable satellite image fragment within each agricultural field. NDVI values one third of the field area and lower than the other two thirds were considered low (FIG. 2).
- An independent verification of the method was carried out on six agricultural fields on an area of 713.3 hectares. The content of humus and the thickness of the humus horizon were determined at 42 ground points (Fig. 3). During testing, the method gave 12.5% type I errors (false positives) and 3.8% type II errors (false negatives).
- the table shows the definition of the degree of soil degradation according to various criteria in the field measurements.
- the probability of detecting actual degradation by field measurements was 87.5%.
- the probability of detecting soil degradation by field measurements outside the predicted areas of soil degradation was 3.8%.
- the results show that the use of a neural network is possible for the selection of satellite images suitable for the calculation of vegetation indices and the subsequent identification of degradation sites based on the processing of multi-temporal satellite images. This eliminates the need for intermediate filtering systems when selecting satellite images with difficulties in identifying clouds, cloud shadows, and open soil (Fig. 1).
- a direct selection by the neural network of Landsat satellite images suitable for calculations was made. An example of calculating the soil degradation map.
- the agricultural field was divided into three equal areas with NDVI values in the low, medium, and high ranges. Then the zones of medium and high NDVI values were assigned a value of "0", and the zone of low NDVI values was assigned a value of "1".
- a series of binary maps of the distribution of low NDVI values was obtained for each agricultural field. Then, the values of binary maps for each pixel were summed and divided by the number of Landsat satellite imagery scenes selected for the agricultural field: where
- An AOLNDVI value > 0.5 was taken as a soil degradation zone. By dividing by a threshold value of 0.5, a binary soil degradation map was generated (FIG. 3).
- Ground check example Ground verification was carried out by classical methods of field research of soils. First, topographic maps and satellite images were analyzed. Then field routes and field survey sites were planned. At each point of the field survey, a soil section was laid, the soil profile was described, and soil samples were taken (Figs. 3, 4). The sampling coordinates and the location of the sections are fixed by GPS. The samples were then analyzed in the laboratory. Two indicators were measured - the thickness of the humus horizon and the content of humus in the plow horizon (shown in the table).
- the accuracy of interpretation was determined by the percentage of coincidence of points of ground-based determination of the presence of soil degradation and soil degradation maps inside agricultural fields obtained by automated processing of multi-time satellite images (shown in the table).
- Field measurements show that the map of soil cover degradation, obtained on the basis of processing multi-temporal satellite images, is significantly more accurate than the traditional soil map.
- the probability of detecting non-eroded soils on the contours of a traditional soil map is 50%, while on binary maps of soil degradation obtained on the basis of processing multi-temporal satellite images, this accuracy is 87.5%.
- the proposed method for generating soil degradation maps can be used in automated mapping of degraded soils.
- the proposed technical solution allows to solve the problem of clarification and optimization of cartographic information for agricultural purposes.
Landscapes
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Physics & Mathematics (AREA)
- General Physics & Mathematics (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Remote Sensing (AREA)
- Theoretical Computer Science (AREA)
- Radar, Positioning & Navigation (AREA)
- Bioinformatics & Cheminformatics (AREA)
- General Engineering & Computer Science (AREA)
- Evolutionary Biology (AREA)
- Data Mining & Analysis (AREA)
- Multimedia (AREA)
- Computer Vision & Pattern Recognition (AREA)
- Bioinformatics & Computational Biology (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Evolutionary Computation (AREA)
- Artificial Intelligence (AREA)
- Food Science & Technology (AREA)
- Medicinal Chemistry (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Image Processing (AREA)
Abstract
Description
Способ генерации карт деградации почвенного покрова Method for generating soil degradation maps
Заявляемое в качестве изобретения техническое решение относится к области сельского хозяйства, а именно к точному прецизионному координатному земледелию, и предназначено для использования глубокого машинного обучения (нейросетей) при отборе спутниковых снимков за многолетний период с целью создания карт деградации почвенного покрова, отражающих участки деградации внутри сельскохозяйственных полей. The technical solution claimed as an invention relates to the field of agriculture, namely to precise precision coordinate farming, and is intended for the use of deep machine learning (neural networks) in the selection of satellite images over a long period in order to create soil degradation maps that reflect degradation areas within agricultural fields.
Использование спутниковой информации широко распространено в настоящее время в сельскохозяйственных работах. Спутниковые снимки помогают получать в динамике информацию о сельскохозяйственных угодьях и вовремя реагировать на возникающие отклонения. В настоящее время развитие космических технологий мониторинга расширило возможности оперативного отслеживания состояния земель сельскохозяйственного назначения. Использование данных спутниковой информации позволяет повысить точность измерения биометрических показателей полей, что с применением нейросетей дает возможность провести интерполирование значений этих показателей за многолетний период, причем в кратчайшие сроки. Задача получения интегральной характеристики изменений почвы за десятки лет является актуальной. Интегральными характеристиками являются значения коэффициентов мультивременной линии почв. Сверка вычислительных данных с эмпирически полученными в результате осмотра конкретного поля на месте позволяет максимально избежать получения не уточненной информации. The use of satellite information is now widespread in agricultural work. Satellite images help to obtain dynamic information about agricultural land and respond in time to emerging deviations. At present, the development of space monitoring technologies has expanded the possibilities of operational tracking of the state of agricultural land. The use of satellite information data makes it possible to increase the accuracy of measuring biometric indicators of fields, which, using neural networks, makes it possible to interpolate the values of these indicators over a long period, and in the shortest possible time. The task of obtaining an integral characteristic of soil changes over decades is relevant. The integral characteristics are the values of the coefficients of the multitemporal line of soils. Reconciliation of computational data with empirical data obtained as a result of inspecting a particular field on the spot makes it possible to avoid obtaining unspecified information as much as possible.
Картирование участков деградации почвенного покрова - сложная и трудоемкая процедура. Деградацию можно предсказать, моделируя процессы деградации и получая характеристики местности из топографических карт и цифровых моделей рельефа. Места развития деградации, спрогнозированные с помощью моделирования, требуют дальнейшего подтверждения, поскольку при одинаковых топографии и климате деградация может произойти, а может и не произойти. Деградацию можно обнаружить на основе анализа большого количества спутниковых снимков в режиме ручной интерпретации. В этом случае точность обнаружения и определения границ деградированных территорий выше, чем при наземных съемках. К основным недостаткам ручной интерпретации большого количества спутниковых снимков можно отнести высокую стоимость высококвалифицированного человеческого труда, не поддающегося автоматизации, и низкую производительность. Современные тенденции в автоматизации выявления и картирования участков деградации почвенного покрова основаны на анализе вегетационных индексов растительности, при анализе которых возникают проблемы, если они проводятся в автоматическом режиме отбора пригодных для расчетов снимков. Например, маски облаков находятся в архивах спутниковых снимков, но обычно этих масок недостаточно для диагностики наличия или отсутствия облаков на спутниковых снимках, а включение в обработку мультивременной спутниковой съемки даже одного не пригодного снимка полностью искажает результаты расчета. Современная тенденция отбора спутниковых снимков основана на использовании глубокого машинного обучения, которое позволяет выбрать необходимые спутниковые снимки. Mapping areas of soil degradation is a complex and time-consuming procedure. Degradation can be predicted by modeling degradation processes and obtaining terrain characteristics from topographic maps and digital elevation models. Degradation sites predicted by modeling require further confirmation, as degradation may or may not occur under the same topography and climate. Degradation can be detected based on the analysis of a large number of satellite images in the manual interpretation mode. In this case, the accuracy of detection and determination of the boundaries of degraded territories is higher than in land-based surveys. The main disadvantages of manual interpretation of a large number of satellite images include the high cost of highly skilled human labor, which cannot be automated, and low productivity. Modern trends in automating the identification and mapping of areas of soil degradation are based on the analysis of vegetation indices of vegetation, the analysis of which causes problems if they are carried out in the automatic mode of selecting images suitable for calculations. For example, cloud masks are found in archives of satellite images, but usually these masks are not enough to diagnose the presence or absence of clouds on satellite images, and including even one unsuitable image in the processing of multi-time satellite imagery completely distorts the calculation results. The current trend in selecting satellite images is based on the use of deep machine learning, which allows you to select the necessary satellite images.
Распознавание образов является одной из наиболее востребованных задач искусственного интеллекта и может найти применение в самых различных прикладных областях. Наиболее широко для распознавания образов в настоящее время используются нейросети. Они, в ряде случаев, показывают результаты сравнимые или превосходящие возможности человека в решении аналогичных задач. Но в ряде случаев расширение их использования сдерживается трудностью интерпретации полученного решения. Действительно, для ряда наиболее ответственных применений нормативно требуется или, естественно, ожидается верификация и одобрение/отклонение человеком автоматического решения. Pattern recognition is one of the most demanded tasks of artificial intelligence and can be used in a wide variety of application areas. Neural networks are currently used most widely for pattern recognition. In some cases, they show results comparable or superior to human capabilities in solving similar problems. But in a number of cases, the expansion of their use is hindered by the difficulty of interpreting the resulting solution. Indeed, for a number of the most critical applications, verification and human approval/rejection of the automatic solution is required or naturally expected.
Глубокое машинное обучение в виде сверточных нейронных сетей получает все большее распространение в различных областях научно-технической деятельности. Нейронные сети используются для расчета и оценки изменений в землепользовании за длительные периоды времени (1984 год - настоящее время). Во многих случаях использование нейронных сетей позволяет добиться большей точности расчетов, чем традиционные методы исследования явлений, с меньшими трудозатратами. В последние годы новый подход компьютерного зрения на основе нейронных сетей успешно применяется при решении различных задач с помощью спутниковых снимков. Таким образом, использование сверточных нейронных сетей (CNN) для обработки цветных изображений земной поверхности обеспечило высокую точность распознавания различных почвенных процессов. Deep machine learning in the form of convolutional neural networks is becoming more widespread in various fields of scientific and technical activity. Neural networks are used to calculate and evaluate changes in land use over long periods of time (1984 - present). In many cases, the use of neural networks makes it possible to achieve greater accuracy of calculations than traditional methods of studying phenomena, with less labor. In recent years, a new computer vision approach based on neural networks has been successfully applied in solving various problems using satellite images. Thus, the use of convolutional neural networks (CNN) for processing color images of the earth's surface provided high accuracy in the recognition of various soil processes.
Известен предшествующий аналог заявляемого технического решения, способ дистанционного определения состояния и использования земель сельскохозяйственного назначения по заявке России на изобретение N°2018111761от 02.04.2018г., МПК: G01 W 1/00, G01W 1/08, опубликованной 04.10.2019г. В аналоге описано информационно-управляющее средство и автоматизированная система мониторинга земель сельскохозяйственного назначения, при которых используют беспилотные летательные аппараты самолетного типа с размещенными на них мультиспектральными камерами, а также наземное оборудование в виде мультиспектральной камеры и тепловизора, установленное на передвижной вышке на земле, позволяющие производить опережающую съемку и выделять участки под детальные исследования площадей деградированных земель, подверженных водной и ветровой эрозии и переувлажнению. A prior analogue of the claimed technical solution is known, a method for remotely determining the state and use of agricultural land according to the Russian application for invention N ° 2018111761 of 04/02/2018, IPC: G01 W 1/00, G01W 1/08 published on 04.10.2019 The analog describes an information management tool and an automated system for monitoring agricultural land, which use unmanned aerial vehicles of an aircraft type with multispectral cameras placed on them, as well as ground equipment in the form of a multispectral camera and a thermal imager installed on a mobile tower on the ground, allowing to produce advance survey and allocate areas for detailed studies of areas of degraded land subject to water and wind erosion and waterlogging.
Несмотря на очевидные различия в применяемой технике, общим признаком с заявляемым техническим решением является создание карт с целью определения мест дислокации эродированных почв. Despite the obvious differences in the technique used, a common feature with the proposed technical solution is the creation of maps to determine the location of eroded soils.
Недостатки данного аналога связаны с целью его разработки, в основном направленной на повышение результативности интерпретации почвенного покрова. Аналог характеризует предшествующее поколение способов диагностики почвы с проведением спектральной съемки и сбором тематических картографических материалов с помощью летательных аппаратов. В данном аналоге по заявке России на изобретение Ne 2018111761 не предусматривается анализ мультивременных рядов спутниковой съемки с использованием нейросетей. The disadvantages of this analogue are associated with the purpose of its development, mainly aimed at improving the effectiveness of the interpretation of the soil cover. The analogue characterizes the previous generation of methods for diagnosing soil with spectral survey and collection of thematic cartographic materials using aircraft. This analogue according to the Russian application for the invention Ne 2018111761 does not provide for the analysis of multi-time series of satellite imagery using neural networks.
Известен аналог нового поколения (прототип), способ предуборочной десикации посевов сельскохозяйственных культур переменной нормой внутри одного поля по патенту России на изобретение М?2717933 от 17.07.2019г., МПК: A01D 45/00, опубликованному 26.03.2020г., включающий автоматизированную работу сельскохозяйственного оборудования с применением спутниковой навигации для индивидуального анализа внутриполевых зон, предварительно запроектированных на картографическом контуре поля, и расчет дозирования препарата, вносимого для улучшения параметров поля, засеянного сельскохозяйственными культурами, причем по отдельно взятому полю предварительно разработанную агрономом карту-задание на основе значений вегетационного индекса NDVI и на основе определения нормы рабочего раствора при визуальном осмотре поля загружают в бортовой компьютер, установленный в кабине опрыскивателя, далее с помощью бортового компьютера устанавливают геолокацию посредством системы ГПС/ГЛОНАСС, а бортовой компьютер в процессе работы опрыскивателя считывает нормы с карты-задания в конкретной точке поля и в процессе десикации корректирует норму расхода рабочего раствора препарата на каждом участке поля согласно загруженной карте-заданию при проведении десикации следующим образом: An analogue of a new generation (prototype) is known, a method for pre-harvest desiccation of crops with a variable rate within one field according to the Russian patent for the invention M? equipment using satellite navigation for individual analysis of intra-field zones, previously designed on the cartographic contour of the field, and calculation of the dosage of the drug applied to improve the parameters of the field sown with crops, and for a single field, a task map previously developed by an agronomist based on the values of the vegetation index NDVI and based on the determination of the norm of the working solution during visual inspection, the fields are loaded into the on-board computer installed in the sprayer cabin, then using the on-board computer, geolocation is established using the GPS / GLONASS system, and the on-board computer in the process e sprayer operation reads the norms from the task card at a specific point in the field and in in the process of desiccation, adjusts the rate of consumption of the working solution of the drug in each section of the field according to the loaded map-task during desiccation as follows:
— исходя из трех внутриполевых зон с корректировкой нормы рабочего раствора согласно схеме: - для зоны ДО°1 - NDVI < 0,2 - норма рабочего раствора от 0 до 50%;- для зоны ДО?2 - NDVI от 0,2 до 0,45 - норма рабочего раствора от 50 до 100%;- для зоны ДО°3 - NDVI>0,45 - норма рабочего раствора от 100 до 125%; - based on three intrafield zones with adjustment of the norm of the working solution according to the scheme: - for the zone DO ° 1 - NDVI < 0.2 - the norm of the working solution is from 0 to 50%; - for the zone DO? 2 - NDVI from 0.2 to 0 ,45 - the rate of the working solution from 50 to 100%; - for the zone DO ° 3 - NDVI> 0.45 - the rate of the working solution from 100 to 125%;
— исходя из четырех внутриполевых зон с корректировкой нормы рабочего раствора, согласно схеме:- для зоны ДО°1 - NDVI<0,2 - норма рабочего раствора от 0 до 50%;- для зоны ДО? 2 - NDVI от 0,2 до 0,3 - норма рабочего раствора от 50 до 75%;- для зоны N°3 . NDVI от 0,3 до 0,45 - норма рабочего раствора от 75 до 100%;- для зоны ДО°4 . NDVI>0,45 - норма рабочего раствора от 100 до 125%, и далее проводят обработку всего поля согласно разработанной карте-заданию с установленными нормами рабочего раствора. - based on four intrafield zones with adjustment of the norm of the working solution, according to the scheme: - for the zone DO ° 1 - NDVI <0.2 - the norm of the working solution is from 0 to 50%; - for the zone DO? 2 - NDVI from 0.2 to 0.3 - working solution rate from 50 to 75%; - for zone N ° 3. NDVI from 0.3 to 0.45 - the norm of the working solution from 75 to 100%; - for the zone DO ° 4. NDVI>0.45 - the norm of the working solution is from 100 to 125%, and then the entire field is processed according to the developed task map with the established norms of the working solution.
Техническое решение патента РФ ДО°2717933 обладает признаками сходства с заявляемым техническим решением, такими как создание карт внутриполевой неоднородности поля с помощью спутниковой информации. The technical solution of the RF patent DO°2717933 has signs of similarity with the claimed technical solution, such as the creation of maps of the field inhomogeneity of the field using satellite information.
Однако относительно узкий диапазон применения (десикация), и то, что способ- прототип не позволяет проводить анализ электронного картирования в мультивременном режиме, снижает эффективность способа-прототипа, в то время как в заявляемом решении отбор спутниковых снимков осуществляется за многолетний период. Сходством является исследование вегетационного индекса NDVI, однако в прототипе этот индекс считают один раз, по анализу одного кадра космической съемки, а в заявляемом техническом решении индекс NDVI рассчитывают для каждого поля для каждого снимка за промежуток времени с 1984 года. Частота встречаемости низкого NDVI в заявляемом решении показывает участки не со случайными, а с устойчивыми ежегодными проблемами в развитии растений, соответственно достигается возможность с наибольшей точностью определять места дислокации деградации почвенного покрова. However, the relatively narrow range of application (desiccation), and the fact that the prototype method does not allow the analysis of electronic mapping in multi-time mode, reduces the effectiveness of the prototype method, while in the claimed solution, satellite imagery is selected over a multi-year period. The similarity is the study of the NDVI vegetation index, however, in the prototype, this index is calculated once, according to the analysis of one frame of a satellite imagery, and in the claimed technical solution, the NDVI index is calculated for each field for each image for a period of time since 1984. The frequency of occurrence of low NDVI in the proposed solution shows areas not with random, but with persistent annual problems in the development of plants, respectively, the ability to determine the location of soil degradation with the greatest accuracy is achieved.
Цель заявляемого технического решения - на основе обработки мультивременных спутниковых снимков достижение возможности картографирования участков деградации почвенного покрова внутри сельскохозяйственных полей. Техническая задача - создание достоверного и максимально приближенного к реальности картографического представления результатов анализа мультивременных спутниковых снимков, для чего разработан заявляемый способ. The purpose of the proposed technical solution is based on the processing of multi-temporal satellite images to achieve the possibility of mapping areas of soil degradation within agricultural fields. The technical task is to create a reliable and as close as possible to reality cartographic representation of the results of the analysis of multi-temporal satellite images, for which the claimed method has been developed.
В процессе апробирования способа производилась индикация деградированных площадей пашни на основе отбора спутниковых снимков методами глубокого машинного обучения и методов расчета средней встречаемости низких значений вегетационного индекса NDVI. In the process of testing the method, degraded areas of arable land were indicated based on the selection of satellite images using deep machine learning methods and methods for calculating the average occurrence of low values of the vegetation index NDVI.
Технический результат - расширение эксплуатационных возможностей картографирования и автоматизация процесса распознавания деградированных участков почвенного покрова внутри сельскохозяйственных полей с применением на практике оптимальных параметров способа создания карт деградации почвенного покрова по результатам обработки мультивременных спутниковых снимков. Работа блока обучения тракта нейросетевого распознавания, обеспечивающего конечное классификационное решение по исследуемым картам полей, повышает вероятность правильной классификации спутниковой информации, а последующая верификация на поле позволяет максимально улучшить точность получаемых карт. Достижение указанного результата обеспечивается особенностями заявляемого способа. EFFECT: expanding the operational capabilities of mapping and automating the process of recognizing degraded soil cover areas inside agricultural fields using in practice the optimal parameters of the method for creating maps of soil cover degradation based on the results of processing multi-time satellite images. The operation of the training unit of the neural network recognition path, which provides the final classification solution for the studied field maps, increases the probability of correct classification of satellite information, and subsequent verification on the field allows to maximize the accuracy of the resulting maps. The achievement of this result is ensured by the features of the proposed method.
Сущность заявляемого технического решения состоит в том, что способ генерации карт деградации почвенного покрова на основе обработки мультивременных спутниковых снимков включает создание карт деградации почвенного покрова с помощью спутниковой информации, при котором скачивают спутниковые снимки Landsat, для каждой исследуемой точки поверхности Земли с различных кадров космической съемки за много лет, далее с помощью обучаемой нейронной сети отбирают снимки, не имеющие дефектов, препятствующих расчетам вегетационных индексов, рассчитывают вегетационный индекс NDVI для каждого пригодного снимка, рассчитывают с помощью принципа двоичной логики и измерения частоты встречаемости двоичного атрибута среднюю встречаемость низких значений NDVI (AOLNDVI), составляют бинарную карту развития деградации почвенного покрова внутри сельскохозяйственного поля и проводят эмпирические полевые замеры мощности гумусового горизонта для верификации полученных результатов. The essence of the proposed technical solution lies in the fact that the method of generating maps of soil degradation based on the processing of multi-temporal satellite images includes the creation of maps of soil cover degradation using satellite information, in which Landsat satellite images are downloaded for each studied point on the Earth's surface from different frames of satellite imagery for many years, then with the help of a trained neural network, images are selected that do not have defects that prevent the calculation of vegetation indices, the vegetation index NDVI is calculated for each suitable image, the average occurrence of low NDVI values (AOLNDVI ), make a binary map of the development of soil cover degradation within the agricultural field and conduct empirical field measurements of the thickness of the humus horizon to verify the results obtained.
В заявленном способе последовательно применяются принципы двоичной логики и измерения частоты встречаемости двоичного атрибута (низкого значения NDVI) в большом количестве спутниковых снимков. Проявление бинарного признака каждого конкретного спутникового снимка не является при таком подходе самостоятельной характеристикой. The claimed method consistently applies the principles of binary logic and measurement of the frequency of occurrence of a binary attribute (low NDVI value) in a large number of satellite images. The manifestation of a binary feature of each specific satellite image is not an independent characteristic in this approach.
Действительно, низкие значения NDVI в каждый конкретный год могут быть связаны с факторами деградации почвы, колебаниями погоды, недостатками сельскохозяйственных технологий, свойствами конкретной культуры и т. д. Совершенно иная ситуация возникает при анализе набора бинарных карт низких значений NDVI за 35 лет и более для одной и той же территории. Если на десятках спутниковых снимков Landsat за 35 лет значение пикселя чаще всего (более чем на 50% сцен) попало в зону низкого значения NDVI, то можно предположить, что плодородие почвы в этой части поля снижено. В участках с низким плодородием почв можно предположить наличие деградации почвенного покрова. Это предположение подтвердилось в ходе проверки способа методом полевых замеров мощности гумусового горизонта. Indeed, low NDVI values in any particular year can be associated with soil degradation factors, weather fluctuations, deficiencies in agricultural technologies, properties of a particular crop, etc. A completely different situation arises when analyzing a set of binary maps of low NDVI values for 35 years or more for the same territory. If on dozens of Landsat satellite images over 35 years the pixel value most often (on more than 50% of scenes) fell into the zone of low NDVI value, then it can be assumed that soil fertility in this part of the field is reduced. In areas with low soil fertility, degradation of the soil cover can be assumed. This assumption was confirmed during the verification of the method by the method of field measurements of the thickness of the humus horizon.
Заявляемый способ проиллюстрирован рисунками фиг.1-4 и таблицей, на которых изображены: The inventive method is illustrated by figures 1-4 and a table showing:
Фиг.1 - Пригодные и не пригодные для расчетов вегетационных индексов снимки, сортируемые нейросетью, где: 1 - пригодные для расчетов; 2 - не пригодные по причине облачности; 3 - не пригодные по причине тени от облаков; 4 - не пригодные по причине вымокания части посевов; 5 - не пригодные по причине отсутствия вегетации сельскохозяйственных культур; 6 - не пригодные по причине снежного покрова; 7 - не пригодные по причине покрытия пожнивными остатками; 8 - не пригодные по причине наличия горения и продуктов горения; 9 - 14 - не пригодные по причине наличия ошибок агротехники. Figure 1 - Suitable and not suitable for calculating vegetation indices, images sorted by a neural network, where: 1 - suitable for calculations; 2 - not suitable due to cloudiness; 3 - unusable due to cloud shadows; 4 - parts of crops not suitable due to wetting; 5 - unsuitable due to the lack of crop vegetation; 6 - unsuitable due to snow cover; 7 - unsuitable due to coverage with crop residues; 8 - not suitable due to the presence of combustion and combustion products; 9 - 14 - not suitable due to the presence of errors in agricultural technology.
Фиг.2 - Этапы расчета карты деградации почв, где: 1 - расчет карт NDV1 для каждого поля и каждой сцены Landsat, отобранные нейросетью; 2 - выделение области низких значений NDV1 для каждой карты NDVI (одна треть от площади карты); 3 - расчет карты средней встречаемости низких значений NDVI; 4 - построение бинарной карты распространения деградации почв, где более 50% раз за 35 лет встречались низкие значения NDVI. Fig.2 - Stages of calculating soil degradation maps, where: 1 - calculation of NDV1 maps for each field and each Landsat scene, selected by the neural network; 2 - highlighting the area of low NDV1 values for each NDVI map (one third of the map area); 3 - calculation of the map of the average occurrence of low NDVI values; 4 - construction of a binary map of the distribution of soil degradation, where more than 50% of the times in 35 years low NDVI values were encountered.
Фиг.З - Бинарная карта деградации почвенного покрова, построенная на основе обработки мультивременных спутниковых снимков, отобранных нейросетью, и точки проведения полевых замеров мощности гумусового горизонта для верификации полученных результатов (номерами проставлены точки полевых замеров результаты обработки, которых представлены в таблице). Зеленое - территории с прогнозируемым отсутствием проявления деградации, красное - участки потенциальной деградации почвенного покрова. Fig.3 - Binary map of soil degradation, built on the basis of processing multi-temporal satellite images selected by the neural network, and the points of field measurements of the thickness of the humus horizon to verify the results obtained (the numbers indicate the points of field measurements, the results of processing, which presented in the table). Green - areas with a predicted absence of degradation, red - areas of potential degradation of the soil cover.
Фиг.4 - Традиционная почвенная карта и места проведения полевых замеров (номерами проставлены точки полевых замеров результаты обработки, которых представлены в таблице). Цифры в кружках на традиционной почвенной карте означают: 2 - отсутствие деградации, 3 - слабую ветровую деградацию, 4 - слабую водную деградацию, 6 - среднюю водную деградацию, 7 - сильную водную деградацию, 9 - почвы другого типа. Fig.4 - Traditional soil map and locations of field measurements (the numbers indicate the points of field measurements, the results of processing, which are presented in the table). The numbers in circles on a traditional soil map mean: 2 - no degradation, 3 - weak wind degradation, 4 - weak water degradation, 6 - medium water degradation, 7 - strong water degradation, 9 - soils of another type.
ПРИМЕР конкретного выполнения заявляемого способа. An EXAMPLE of a specific implementation of the proposed method.
При конкретном применении заявляемого способа зоны деградации почвы были рассчитаны на основе частоты появления низких значений NDVI в период с 1984 по 2021 г. Низкие значения NDVI рассчитывались отдельно для каждого подходящего фрагмента спутникового изображения в границах каждого сельскохозяйственного поля. Значения NDVI одной трети площади поля и ниже, чем другие две трети, считались низкими (фиг. 2). Независимая проверка способа проводилась на шести сельскохозяйственных полях на площади 713,3 га. Содержание гумуса и мощность гумусового горизонта определяли в 42 наземных точках (фиг. 3). В ходе тестирования метод дал 12,5% ошибок I типа (ложноположительные) и 3,8% ошибок II типа (ложноотрицательные). Таблица показывает определение степени деградации почвы по различным критериям в местах полевых замеров. For a specific application of the proposed method, soil degradation zones were calculated based on the frequency of occurrence of low NDVI values from 1984 to 2021. Low NDVI values were calculated separately for each suitable satellite image fragment within each agricultural field. NDVI values one third of the field area and lower than the other two thirds were considered low (FIG. 2). An independent verification of the method was carried out on six agricultural fields on an area of 713.3 hectares. The content of humus and the thickness of the humus horizon were determined at 42 ground points (Fig. 3). During testing, the method gave 12.5% type I errors (false positives) and 3.8% type II errors (false negatives). The table shows the definition of the degree of soil degradation according to various criteria in the field measurements.
ТаблицаTable
Определение степени деградации почвы по различным критериям в местах полевых замеров наличие деградации по данным почвенный покров наземного обследования на основе: относится к Determination of the degree of soil degradation according to various criteria in the field measurements.
Номер мощность деградированному по почвенн гумусового содержа содержа мощность оба карте деградации ого горизонта, ние гумусового ние фактор построенной на основе тип разреза см са о а , гумуса горизонта нейросети деградации*The number of the thickness of the degraded soil humus content containing the thickness of both the degradation map of the th horizon, the lower humus factor, and the factor built on the basis of the type of section cmsaoa , humus horizon degradation neural networks*
1 75 4.1 п1 75 4.1 p
2 80 4.3 п2 80 4.3 p
3 81 4.4 - - п3 81 4.4 - - p
4 70 4.7 - - п4 70 4.7 - - p
5 45 3.5 + - + + d5 45 3.5 + - + + d
6 43 3.0 + + + е6 43 3.0 + + + e
7 78 3.1 + п7 78 3.1 + p
8 61 3.4 - - п8 61 3.4 - - p
9 31 2.8 + + + + е9 31 2.8 + + + + e
10 67 3.5 п 11 64 3.7 - - п 12 27 2.6 + + + + Е 10 67 3.5 p 11 64 3.7 - - p 12 27 2.6 + + + + Е
*тип деградации: n - нет деградации; е - ветровая эрозия; d - водная эрозия. *type of degradation: n - no degradation; e - wind erosion; d - water erosion.
На участках деградации почвенного покрова, выявленных предложенным способом, вероятность выявления фактической деградации полевыми замерами составила 87,5%. Вероятность обнаружения деградации почвы полевыми замерами за пределами прогнозируемых участков деградации почвенного покрова составила 3,8%. Результаты показывают, что применение нейросети возможно для отбора пригодных к расчету вегетационных индексов спутниковых снимков и последующего выявления участков деградации на основе обработки мультивременных спутниковых снимков. Это устраняет необходимость в промежуточных системах фильтрации при выборе спутниковых снимков с трудностями определения облаков, теней от облаков, открытой поверхности почвы (фиг. 1). Произведен прямой выбор нейросетью пригодных для расчетов спутниковых снимков Landsat. Пример расчета карты деградации почвенного покрова. In the areas of soil degradation identified by the proposed method, the probability of detecting actual degradation by field measurements was 87.5%. The probability of detecting soil degradation by field measurements outside the predicted areas of soil degradation was 3.8%. The results show that the use of a neural network is possible for the selection of satellite images suitable for the calculation of vegetation indices and the subsequent identification of degradation sites based on the processing of multi-temporal satellite images. This eliminates the need for intermediate filtering systems when selecting satellite images with difficulties in identifying clouds, cloud shadows, and open soil (Fig. 1). A direct selection by the neural network of Landsat satellite images suitable for calculations was made. An example of calculating the soil degradation map.
Для каждого расчета NDVI сельскохозяйственное поле было разделено на три равные площади со значениями NDVI в низком, среднем и высоком диапазонах. Затем зонам средних и высоких значений NDVI было присвоено значение «0», а зоне низких значений NDVI было присвоено значение «1». Была получена серия бинарных карт распределения низких значений NDVI для каждого сельскохозяйственного поля. Затем производили суммирование значений бинарных карт для каждого пикселя и деление на количество сцен спутниковых снимков Landsat, выбранных для сельскохозяйственного поля: где For each NDVI calculation, the agricultural field was divided into three equal areas with NDVI values in the low, medium, and high ranges. Then the zones of medium and high NDVI values were assigned a value of "0", and the zone of low NDVI values was assigned a value of "1". A series of binary maps of the distribution of low NDVI values was obtained for each agricultural field. Then, the values of binary maps for each pixel were summed and divided by the number of Landsat satellite imagery scenes selected for the agricultural field: where
• AOLNDVI - средняя встречаемость низких значений NDVI; • AOLNDVI - average occurrence of low NDVI values;
• LNDVIi - индикатор нижней зоны NDVI для i-й сцены Landsat; • LNDVIi - indicator of the lower NDVI zone for the i-th scene of Landsat;
• п - количество сцен Landsat, выбранных для расчетов. • n - the number of Landsat scenes selected for calculations.
Значение AOLNDVI> 0,5 было принято за зону деградации почвы. Делением на пороговое значение 0,5, была создана бинарная карта деградации почвенного покрова (Фиг.З). An AOLNDVI value > 0.5 was taken as a soil degradation zone. By dividing by a threshold value of 0.5, a binary soil degradation map was generated (FIG. 3).
Пример наземной проверки. Наземная верификация проводилась классическими методами полевых исследований почв. Вначале анализировали топографические карты и спутниковые снимки. Затем были запланированы полевые маршруты и места полевого обследования. В каждой точке полевого обследования закладывали почвенный разрез, был описан почвенный профиль и взяты почвенные пробы (фиг. 3, 4). Координаты отбора проб и расположение разрезов зафиксированы по GPS. Далее был проведен анализ проб в лаборатории. Измеряли два показателя - мощность гумусового горизонта и содержание гумуса в пахотном горизонте (показаны на таблице). Ground check example. Ground verification was carried out by classical methods of field research of soils. First, topographic maps and satellite images were analyzed. Then field routes and field survey sites were planned. At each point of the field survey, a soil section was laid, the soil profile was described, and soil samples were taken (Figs. 3, 4). The sampling coordinates and the location of the sections are fixed by GPS. The samples were then analyzed in the laboratory. Two indicators were measured - the thickness of the humus horizon and the content of humus in the plow horizon (shown in the table).
Точность интерпретации определялась процентом совпадения точек наземного определения наличия деградации почв и карт деградации почвенного покрова внутри сельскохозяйственных полей, полученных автоматизированным способом обработки мультивременных спутниковых снимков (показаны в таблице). Полевые замеры показывают, что карта деградации почвенного покрова, полученная на основе обработки мультивременных спутниковых снимков, существенно точнее традиционной почвенной карты. Вероятность обнаружить неэродированные почвы на контурах традиционной почвенной карты составляет 50%, в то время как на бинарных картах деградации почвенного покрова, полученных на основе обработки мультивременных спутниковых снимков, эта точность составляет 87,5%. Исходя из вышеизложенного, можно сделать вывод о том, что в заявляемом техническом решении разработан новый способ генерации карт деградации почвенного покрова на основе обработки мультивременных спутниковых снимков. The accuracy of interpretation was determined by the percentage of coincidence of points of ground-based determination of the presence of soil degradation and soil degradation maps inside agricultural fields obtained by automated processing of multi-time satellite images (shown in the table). Field measurements show that the map of soil cover degradation, obtained on the basis of processing multi-temporal satellite images, is significantly more accurate than the traditional soil map. The probability of detecting non-eroded soils on the contours of a traditional soil map is 50%, while on binary maps of soil degradation obtained on the basis of processing multi-temporal satellite images, this accuracy is 87.5%. Based on the foregoing, it can be concluded that the proposed technical solution has developed a new method for generating soil degradation maps based on the processing of multi-temporal satellite images.
Предлагаемый способ генерации карт деградации почвенного покрова может быть использован при автоматизированном картировании деградированных почв. The proposed method for generating soil degradation maps can be used in automated mapping of degraded soils.
Заявляемое техническое решение позволяет решать задачи уточнения и оптимизации картографической информации для целей сельского хозяйства. The proposed technical solution allows to solve the problem of clarification and optimization of cartographic information for agricultural purposes.
Подобное сочетание универсальности способа с относительной простотой использования для выявления деградированных участков полей в прототипе не достигнуто. Such a combination of the versatility of the method with the relative ease of use to identify degraded areas of fields in the prototype is not achieved.
Исходя из вышеизложенного, можно сделать вывод о том, что заявляемое техническое решение соответствует критериям «новизна», «изобретательский уровень» и «промышленная применимость». Based on the foregoing, we can conclude that the proposed technical solution meets the criteria of "novelty", "inventive step" and "industrial applicability".
Claims
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| RU2021119664A RU2769575C1 (en) | 2021-07-05 | 2021-07-05 | Method for generating soil degradation maps |
| RU2021119664 | 2021-07-05 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2023282787A1 true WO2023282787A1 (en) | 2023-01-12 |
Family
ID=81076151
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/RU2021/000530 Ceased WO2023282787A1 (en) | 2021-07-05 | 2021-11-30 | Method of generating soil degradation maps |
Country Status (2)
| Country | Link |
|---|---|
| RU (1) | RU2769575C1 (en) |
| WO (1) | WO2023282787A1 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US12499667B2 (en) | 2024-02-26 | 2025-12-16 | Deere & Company | Systems and methods for worksite imagery selection |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN117409333B (en) * | 2023-12-15 | 2024-02-13 | 四川省生态环境科学研究院 | Ecological fragile area identification and ecological restoration method based on remote sensing image |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| RU2265839C1 (en) * | 2004-04-13 | 2005-12-10 | Государственное учреждение Всероссийский научно-исследовательский институт агролесомелиорации | Method of determining soil condition |
| CN106897668A (en) * | 2017-01-20 | 2017-06-27 | 浙江大学 | A kind of Grassland degradation degree extraction method based on remote sensing image |
| CN110175537A (en) * | 2019-05-10 | 2019-08-27 | 深圳大学 | A kind of method and system merging multi-source remote sensing index evaluation Land degradation status |
| CN111666900A (en) * | 2020-06-09 | 2020-09-15 | 中国科学院地理科学与资源研究所 | Method and device for acquiring land cover classification map based on multi-source remote sensing image |
| CN111709379A (en) * | 2020-06-18 | 2020-09-25 | 谢国雪 | Remote sensing image-based hilly area citrus planting land plot monitoring method and system |
-
2021
- 2021-07-05 RU RU2021119664A patent/RU2769575C1/en active
- 2021-11-30 WO PCT/RU2021/000530 patent/WO2023282787A1/en not_active Ceased
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| RU2265839C1 (en) * | 2004-04-13 | 2005-12-10 | Государственное учреждение Всероссийский научно-исследовательский институт агролесомелиорации | Method of determining soil condition |
| CN106897668A (en) * | 2017-01-20 | 2017-06-27 | 浙江大学 | A kind of Grassland degradation degree extraction method based on remote sensing image |
| CN110175537A (en) * | 2019-05-10 | 2019-08-27 | 深圳大学 | A kind of method and system merging multi-source remote sensing index evaluation Land degradation status |
| CN111666900A (en) * | 2020-06-09 | 2020-09-15 | 中国科学院地理科学与资源研究所 | Method and device for acquiring land cover classification map based on multi-source remote sensing image |
| CN111709379A (en) * | 2020-06-18 | 2020-09-25 | 谢国雪 | Remote sensing image-based hilly area citrus planting land plot monitoring method and system |
Non-Patent Citations (1)
| Title |
|---|
| IVANOV E.S., TISHCHENKO I.P., VINOGRADOV A.N.: "Multispectral image segmentation using convolutional neural network", MODERN PROBLEMS OF REMOTE SENSING OF THE EARTH FROM SPACE,, RU, vol. 16, no. 1, 1 January 2019 (2019-01-01), RU, pages 25 - 34, XP093024920, ISSN: 2070-7401, DOI: 10.21046/2070-7401-2019-16-1-25-34 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US12499667B2 (en) | 2024-02-26 | 2025-12-16 | Deere & Company | Systems and methods for worksite imagery selection |
Also Published As
| Publication number | Publication date |
|---|---|
| RU2769575C1 (en) | 2022-04-04 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Halme et al. | Utility of hyperspectral compared to multispectral remote sensing data in estimating forest biomass and structure variables in Finnish boreal forest | |
| Li et al. | Remote estimation of canopy height and aboveground biomass of maize using high-resolution stereo images from a low-cost unmanned aerial vehicle system | |
| KR102496740B1 (en) | System and method for reservoir water body analysis using synthetic aperture radar data | |
| Gruszczyński et al. | Comparison of low-altitude UAV photogrammetry with terrestrial laser scanning as data-source methods for terrain covered in low vegetation | |
| Allouis et al. | Stem volume and above-ground biomass estimation of individual pine trees from LiDAR data: Contribution of full-waveform signals | |
| Guo et al. | Combining GEDI and sentinel data to estimate forest canopy mean height and aboveground biomass | |
| US10621434B2 (en) | Identification and localization of anomalous crop health patterns | |
| EP2927709A1 (en) | Identifying and tracking convective weather cells | |
| CN111028255A (en) | Farmland area pre-screening method and device based on prior information and deep learning | |
| Sanhouse-Garcia et al. | Multi-temporal analysis for land use and land cover changes in an agricultural region using open source tools | |
| CN119085616B (en) | Three-dimensional topography mapping system based on remote sensing technology | |
| Oymatov et al. | Improving the methods of Agricultural mapping using remote sensing data | |
| RU2769575C1 (en) | Method for generating soil degradation maps | |
| Rinnamang et al. | Estimation of aboveground biomass using aerial photogrammetry from unmanned aerial vehicle in teak (Tectona grandis) plantation in Thailand | |
| CN116824157B (en) | Sampling point determination method, remote sensing product authenticity verification method, device and electronic equipment | |
| Brezhnev et al. | Modeling of agricultural spatial objects with heterogeneous dynamically changing spatial structure | |
| Ozdarici-Ok et al. | Object-based classification of multi-temporal images for agricultural crop mapping in Karacabey Plain, Turkey | |
| Hosingholizade et al. | Height estimation of pine (Pinus eldarica) single trees using slope corrected shadow length on unmanned aerial vehicle (UAV) imagery in a plantation forest | |
| Basista et al. | MICRO-MORPHOLOGICAL ANALYSES OF DIGITAL TERRAIN MODEL IN SEARCH OF TRACES OF PLOUGHING ON ARCHAEOLOGICAL OBJECTS | |
| Heckel et al. | The first sub-meter resolution digital elevation model of the Kruger National Park, South Africa | |
| RU2777272C1 (en) | Method for creating soil maps based on the results of the analysis of remote sounding data | |
| Müller et al. | Airborne laser scanning change detection for quantifying geomorphological processes in high mountain regions | |
| Bruggisser | Improving forest mensurations with high resolution point clouds | |
| Sims | Remote sensing data and methods in NFI | |
| Marková et al. | Case Study on Detecting Local Soil Anomalies |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| 121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 21949462 Country of ref document: EP Kind code of ref document: A1 |
|
| WWE | Wipo information: entry into national phase |
Ref document number: 2023/0881.1 Country of ref document: KZ |
|
| NENP | Non-entry into the national phase |
Ref country code: DE |
|
| 122 | Ep: pct application non-entry in european phase |
Ref document number: 21949462 Country of ref document: EP Kind code of ref document: A1 |
|
| WWG | Wipo information: grant in national office |
Ref document number: 2023/0881.1 Country of ref document: KZ |
|
| WWP | Wipo information: published in national office |
Ref document number: 2023/0881.1 Country of ref document: KZ |