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Remote Sensing Technology for Agricultural and Land Management

A special issue of Sensors (ISSN 1424-8220). This special issue belongs to the section "Environmental Sensing".

Deadline for manuscript submissions: 25 May 2025 | Viewed by 4283

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Computer Science Research Centre, University of Surrey, Guildford GU2 7XH, UK
Interests: machine learning; good old fashioned AI; ecological modelling; medical AI; AI and environmental modelling/monitoring
Special Issues, Collections and Topics in MDPI journals

Special Issue Information

Dear Colleagues,

With climate change and biodiversity crises, we need to rethink the way we perform agriculture and land management. Working with nature rather than trying to control it has the potential to increase carbon capture and biodiversity in agricultural units without sacrificing productivity. With regard to the management of the wider landscape, practices in “rewilding” are showing their potential to enhance the ecosystem services such as flood control, water quality, pollination, and amenity that wild spaces provide.

We are still learning how to manage this change effectively. Continuous assessment of land holdings is needed in order to ensure that the management goals are being met. This can only be achieved cost-effectively at scale through the use of remote sensing. This Special Issue will focus on techniques and case studies that build an experience base for the use of remote sensing to manage agricultural units and natural spaces in an environmentally positive and sustainable way.

Submissions of research papers, case studies, and review articles are welcome.

Prof. Dr. Paul Krause
Guest Editor

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Keywords

  • sensor networks
  • Internet of Things
  • environmental monitoring
  • satellite image analysis
  • ecological intensification
  • conservation agriculture
  • ecosystem services
  • biodiversity assessment

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Published Papers (3 papers)

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Research

26 pages, 17954 KiB  
Article
A Large-Scale Agricultural Land Classification Method Based on Synergistic Integration of Time Series Red-Edge Vegetation Index and Phenological Features
by Huansan Zhao, Chunyan Chang, Zhuoran Wang and Gengxing Zhao
Sensors 2025, 25(2), 503; https://doi.org/10.3390/s25020503 - 16 Jan 2025
Viewed by 656
Abstract
Agricultural land classification plays a pivotal role in food security and ecological sustainability, yet achieving accurate large-scale mapping remains challenging. This study presents methodological innovations through a multi-level feature enhancement framework that transcends traditional time series analysis. Using Shandong Province, northern China’s agricultural [...] Read more.
Agricultural land classification plays a pivotal role in food security and ecological sustainability, yet achieving accurate large-scale mapping remains challenging. This study presents methodological innovations through a multi-level feature enhancement framework that transcends traditional time series analysis. Using Shandong Province, northern China’s agricultural heartland, as a case study, we first established a foundation with time series red-edge vegetation indices (REVI) from Sentinel-2 imagery, uniquely combining the normalized difference red edge index (NDRE705) and plant senescence reflectance index (PSRI). Moving beyond conventional time series analysis, we innovatively amplified key temporal characteristics through newly designed spatial feature parameters (SFPs) and phenological feature parameters (PFPs). This strategic enhancement of critical temporal points significantly improved classification performance by capturing subtle spatial patterns and phenological transitions that are often overlooked in traditional approaches. The study yielded three significant findings: (1) The synergistic application of NDRE705 and PSRI significantly outperformed single-index approaches, demonstrating the effectiveness of our dual-index strategy; (2) The integration of SFPs and PFPs with time series REVI markedly enhanced feature discrimination at crucial growth stages, with PFPs showing superior capability in distinguishing agricultural land types through amplified phenological signatures; (3) Our optimal classification scheme (FC6), leveraging both enhanced spatial and phenological features, achieved remarkable accuracy (93.21%) with a Kappa coefficient of 0.9159, representing improvements of 4.83% and 0.0538, respectively, over the baseline approach. This comprehensive framework successfully mapped 120,996 km2 of agricultural land, differentiating winter wheat–summer maize rotation areas (39.44%), single-season crop fields (36.16%), orchards (14.49%), and facility vegetable fields (9.91%). Our approach advances the field by introducing a robust, scalable methodology that not only utilizes the full potential of time series data but also strategically enhances critical temporal features for improved classification accuracy, particularly valuable for regions with complex farming systems and diverse crop patterns. Full article
(This article belongs to the Special Issue Remote Sensing Technology for Agricultural and Land Management)
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Figure 1

Figure 1
<p>Overview of the study area. (The base map data is ESA/world_cover_2020, and the lower left corner displays the DEM of Shandong Province).</p>
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<p>Technical route of the research.</p>
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<p>Phenological information of major agricultural lands in Shandong Province (crop calendar). (Summarization based on statistical information from the Department of Agriculture and Rural Affairs of Shandong Province [<a href="#B49-sensors-25-00503" class="html-bibr">49</a>]). The color changes represent the process of crop growth to decay.</p>
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<p>Schematic diagram of the initial sampling point deployment.</p>
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<p>Classification sample distribution.</p>
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<p>Visualization of NDRE<sub>705</sub> and PSRI time series curves of different agricultural land types in Shandong Province.</p>
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<p>Accuracy of agricultural land classification for different original time series classification schemes.</p>
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<p>Feature importance of SFPs. (It shows the feature importance of the three SFPs in each time phase).</p>
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<p>The 12 PFPs with the highest contribution. (Arranged in descending order of importance).</p>
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<p>Details of the classification of different types of agricultural land. (<b>a1</b>,<b>a2</b>) Winter wheat–summer maize rotation area; (<b>b1</b>,<b>b2</b>) Orchard; (<b>c1</b>,<b>c2</b>) Single-season crop field; (<b>d1</b>,<b>d2</b>) Facility vegetable field. Note: Imagery is a high-resolution Google Earth image from October 2019.</p>
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<p>Distribution of agricultural land types in Shandong Province.</p>
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29 pages, 13171 KiB  
Article
Enhancing Coffee Agroforestry Systems Suitability Using Geospatial Analysis and Sentinel Satellite Data in Gedeo Zone, Ethiopia
by Wondifraw Nigussie, Husam Al-Najjar, Wanchang Zhang, Eshetu Yirsaw, Worku Nega, Zhijie Zhang and Bahareh Kalantar
Sensors 2024, 24(19), 6287; https://doi.org/10.3390/s24196287 - 28 Sep 2024
Cited by 1 | Viewed by 1529
Abstract
The Gedeo zone agroforestry systems are the main source of Ethiopia’s coffee beans. However, land-use and suitability analyses are not well documented due to complex topography, heterogeneous agroforestry, and lack of information. This research aimed to map the coffee coverage and identify land [...] Read more.
The Gedeo zone agroforestry systems are the main source of Ethiopia’s coffee beans. However, land-use and suitability analyses are not well documented due to complex topography, heterogeneous agroforestry, and lack of information. This research aimed to map the coffee coverage and identify land suitability for coffee plantations using remote sensing, Geographic Information Systems (GIS), and the Analytical Hierarchy Process (AHP) in the Gedeo zone, Southern Ethiopia. Remote sensing classifiers often confuse agroforestry and plantations like coffee cover with forest cover because of their similar spectral signatures. Mapping shaded coffee in Gedeo agroforestry using optical or multispectral remote sensing is challenging. To address this, the study identified and mapped coffee coverage from Sentinel-1 data with a decibel (dB) value matched to actual coffee coverage. The actual field data were overlaid on Sentinel-1, which was used to extract the raster value. Pre-processing, classification, standardization, and reclassification of thematic layers were performed to find potential areas for coffee plantation. Hierarchy levels of the main criteria were formed based on climatological, edaphological, physiographic, and socioeconomic factors. These criteria were divided into 14 sub-criteria, reclassified based on their impact on coffee growing, with their relative weights derived using AHP. From the total study area of 1356.2 km2, the mapped coffee coverage is 583 km2. The outcome of the final computed factor weight indicated that average annual temperature and mean annual rainfall are the primary factors, followed by annual mean maximum temperature, elevation, annual mean minimum temperature, soil pH, Land Use/Land Cover (LULC), soil texture, Cation Exchange Capacity (CEC), slope, Soil Organic Matter (SOM), aspect, distance to roads, and distance to water, respectively. The identified coffee plantation potential land suitability reveals unsuitable (413 km2), sub-suitable (596.1 km2), and suitable (347.1 km2) areas. This study provides comprehensive spatial details for Ethiopian cultivators, government officials, and agricultural extension specialists to select optimal coffee farming locations, enhancing food security and economic prosperity. Full article
(This article belongs to the Special Issue Remote Sensing Technology for Agricultural and Land Management)
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Figure 1

Figure 1
<p>Location of the study area.</p>
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<p>Methodological flowchart of the research.</p>
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<p>Pre-processed images (<b>a</b>) sentinel-1 (SAR), and (<b>b</b>) sentinel-2 (MSI).</p>
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<p>Agro-ecological classification, (<b>a</b>) sample field data of coffee coverage, and (<b>b</b>) processed sentinel-1.</p>
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<p>Maps of physiographic thematic layers (<b>a</b>) Elevation, (<b>b</b>) Slope, (<b>c</b>) Aspect, (<b>d</b>) Reclassified elevation, (<b>e</b>) Reclassified slope, (<b>f</b>) Reclassified aspect.</p>
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<p>Maps of edaphological thematic layers. (<b>a</b>) Soil texture, (<b>b</b>) Reclassified soil texture, (<b>c</b>) Soil organic matter, (<b>d</b>) Reclassified soil organic matter, (<b>e</b>) Soil pH, (<b>f</b>) Reclassified soil pH, (<b>g</b>) CEC, (<b>h</b>) Reclassified CEC.</p>
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<p>Maps of climatological thematic layers, (<b>a</b>) Mean annual rainfall, (<b>b</b>) Reclassified mean annual rainfall, (<b>c</b>) Annual mean maximum temperature, (<b>d</b>) Reclassified maximum temperature, (<b>e</b>) Average annual temperature, (<b>f</b>) Reclassified average annual temperature, (<b>g</b>) Annual mean minimum temperature, (<b>h</b>) Reclassified mean minimum temperature.</p>
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<p>Maps of socioeconomic thematic layers, (<b>a</b>) LULC in 2021, (<b>b</b>) Distance to road network, (<b>c</b>) Distance to river network, (<b>d</b>) Reclassified LULC, (<b>e</b>) Reclassified distance to road, (<b>f</b>) Reclassified distance to river.</p>
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<p>Current potential coffee coverage areas in Gedeo zone.</p>
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<p>Identified potential areas for coffee plantation.</p>
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<p>Area coverage of identified potential coffee plantation.</p>
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28 pages, 16525 KiB  
Article
DMAF-NET: Deep Multi-Scale Attention Fusion Network for Hyperspectral Image Classification with Limited Samples
by Hufeng Guo and Wenyi Liu
Sensors 2024, 24(10), 3153; https://doi.org/10.3390/s24103153 - 15 May 2024
Cited by 1 | Viewed by 1453
Abstract
In recent years, deep learning methods have achieved remarkable success in hyperspectral image classification (HSIC), and the utilization of convolutional neural networks (CNNs) has proven to be highly effective. However, there are still several critical issues that need to be addressed in the [...] Read more.
In recent years, deep learning methods have achieved remarkable success in hyperspectral image classification (HSIC), and the utilization of convolutional neural networks (CNNs) has proven to be highly effective. However, there are still several critical issues that need to be addressed in the HSIC task, such as the lack of labeled training samples, which constrains the classification accuracy and generalization ability of CNNs. To address this problem, a deep multi-scale attention fusion network (DMAF-NET) is proposed in this paper. This network is based on multi-scale features and fully exploits the deep features of samples from multiple levels and different perspectives with an aim to enhance HSIC results using limited samples. The innovation of this article is mainly reflected in three aspects: Firstly, a novel baseline network for multi-scale feature extraction is designed with a pyramid structure and densely connected 3D octave convolutional network enabling the extraction of deep-level information from features at different granularities. Secondly, a multi-scale spatial–spectral attention module and a pyramidal multi-scale channel attention module are designed, respectively. This allows modeling of the comprehensive dependencies of coordinates and directions, local and global, in four dimensions. Finally, a multi-attention fusion module is designed to effectively combine feature mappings extracted from multiple branches. Extensive experiments on four popular datasets demonstrate that the proposed method can achieve high classification accuracy even with fewer labeled samples. Full article
(This article belongs to the Special Issue Remote Sensing Technology for Agricultural and Land Management)
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Figure 1

Figure 1
<p>Architecture of the proposed DMAF-NET.</p>
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<p>Multi-scale feature extraction backbone network.</p>
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<p>Three-dimensional multi-scale space–spectral attention enhancement module.</p>
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<p>Four-dimensional pyramid-style multi-scale channel attention module.</p>
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<p>Multi-attention feature fusion module.</p>
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<p>The pseudo-color images and the corresponding ground truth maps for the SA, UP, and IP datasets. (<b>a-1</b>) Pseudo-color map of SA. (<b>a-2</b>) Ground truth map of SA. (<b>b-1</b>) Pseudo-color map of UP. (<b>b-2</b>) Ground truth map of UP. (<b>c-1</b>) Pseudo-color map of IP. (<b>c-2</b>) Ground truth map of IP. (<b>d-1</b>) Pseudo-color map of LK. (<b>d-2</b>) Ground truth map of LK.</p>
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<p>Classification results (%) and training time (seconds) for each dataset under different patch sizes.</p>
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<p>Classification results (%) and training time (seconds) for each dataset with a different number of components retained during PCA operation.</p>
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<p>Classification maps generated by all of the competing methods on the SA dataset with 10 training samples for each category. (<b>a</b>) 3D-CNN. (<b>b</b>) HybridSN. (<b>c</b>) SSRN. (<b>d</b>) Tri-CNN. (<b>e</b>) MCNN-CP. (<b>f</b>) SSFTT. (<b>g</b>) Oct-MCNN-HS. (<b>h</b>) Proposed method.</p>
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<p>Classification maps generated by all of the competing methods on the UP dataset with 10 training samples for each category. (<b>a</b>) 3D-CNN. (<b>b</b>) HybridSN. (<b>c</b>) SSRN. (<b>d</b>) Tri-CNN. (<b>e</b>) MCNN-CP. (<b>f</b>) SSFTT. (<b>g</b>) Oct-MCNN-HS. (<b>h</b>) Proposed method.</p>
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<p>Classification maps generated by all of the competing methods on the IP dataset with 10 training samples for each category. (<b>a</b>) 3D-CNN. (<b>b</b>) HybridSN. (<b>c</b>) SSRN. (<b>d</b>) Tri-CNN. (<b>e</b>) MCNN-CP. (<b>f</b>) SSFTT. (<b>g</b>) Oct-MCNN-HS. (<b>h</b>) Proposed method.</p>
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<p>Classification maps generated by all of the competing methods on the LK dataset with 10 training samples for each category. (<b>a</b>) 3D-CNN. (<b>b</b>) HybridSN. (<b>c</b>) SSRN. (<b>d</b>) Tri-CNN. (<b>e</b>) MCNN-CP. (<b>f</b>) SSFTT. (<b>g</b>) Oct-MCNN-HS. (<b>h</b>) Proposed method.</p>
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<p>Classification results (%) for all competing methods using different amount of training samples on the three datasets; fixed quantity sampling is used for each category. (<b>a-1</b>) The OA of SA dataset. (<b>a-2</b>) The AA of SA dataset. (<b>a-3</b>) The Kappa of SA dataset. (<b>b-1</b>) The OA of UP dataset. (<b>b-2</b>) The AA of UP dataset. (<b>b-3</b>) The Kappa of UP dataset. (<b>c-1</b>) The OA of IP dataset. (<b>c-2</b>) The AA of IP dataset. (<b>c-3</b>) The Kappa of IP dataset. (<b>d-1</b>) The OA of LK dataset. (<b>d-2</b>) The AA of LK dataset. (<b>d-3</b>) The Kappa of LK dataset.</p>
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<p>Classification results (%) for all competing methods using different amount of training samples on the three datasets; fixed proportion sampling is used for each category. (<b>a-1</b>) The OA of SA dataset. (<b>a-2</b>) The AA of SA dataset. (<b>a-3</b>) The Kappa of SA dataset. (<b>b-1</b>) The OA of UP dataset. (<b>b-2</b>) The AA of UP dataset. (<b>b-3</b>) The Kappa of UP dataset. (<b>c-1</b>) The OA of IP dataset. (<b>c-2</b>) The AA of IP dataset. (<b>c-3</b>) The Kappa of IP dataset. (<b>d-1</b>) The OA of LK dataset. (<b>d-2</b>) The AA of LK dataset. (<b>d-3</b>) The Kappa of LK dataset.</p>
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<p>Classification results (%) of ablation experiments.</p>
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<p>The influence of different size convolutional kernels in three branches of baseline.</p>
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<p>The influence of varying numbers of 3D octave convolutions in three branches of baseline.</p>
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<p>Classification results (%) of different dimensionality reduction method.</p>
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