1. Introduction
A pine forest is a coniferous forest in a warm or cool–temperate and subtropical region of China. The ecology of these is wide-ranging. They strengthen the regulation of water, carbon and nitrogen fixation in the soil, improve soil conditions, reduce erosion, and enhance biodiversity [
1]. Pine forests are also sources of timber, resin and other raw materials for the chemical industry, as well as the ecological services listed above [
2]. Therefore, these two are closely related to the stability of the environment and the economic development of mountainous forest areas; among the biological hazards affecting pine forests, pine wilt disease (PWD) is particularly serious [
3]. PWD is a serious forest disease caused by the pine wood nematode Bursaphelenchus xylophilus, and an insect vector for its transmission is the pine sawyer beetle Monochamus alternatus [
4]. A tree that has been infected with disease will be unable to transport water and nutrients to the rest of the tree efficiently. Generally, as a result of the above, the crown will yellow; it will become gradually weakened and eventually die [
5]. As the disease spreads to cover more areas and affects more trees, the damage may also reach all the trees in the forest and cause severe harm to the forest. Traditional monitoring is still mainly done through field observation and experience. These approaches are still feasible for forestry work in practice, but they require considerable labor and time. They are also not suitable for applying in early infection detection across a wide area of the forest uniformly and promptly. Therefore, in time, the damaged trees affected by PWD need to be located, diseased people should be found, the range of the outbreak determined, the transmission paths cut off, infected trees removed, and support for prevention and control provided. This demand is relatively high at the beginning of the infection. At this time, high-speed, high-reliability recognition technology will improve monitoring efficiency, reduce missed and false detections, and prevent further ecological and economic damage. Therefore, this paper will focus on the automatic detection of PWD from satellite remote sensing images for large-scale forest health monitoring [
6].
Forestry staff have been conducting field-based visual inspections for a long time to survey damaged forests. Although this way is simple to understand and directly usable, it is not suitable for a large-area application. The effect of this will be limited by the lack of labor, the inaccessibility of the land, and other physical difficulties. There are many scattered full-coverage surveys in the large mountain forest area, and we cannot react promptly to disease outbreaks. Remotely sensed data may be available for this purpose [
7]. A UAV can take a high-definition, near-ground photograph from above [
8]. However, due to its short flight time and small coverage area, it is not practical for the large-scale, continuous monitoring of many places. Satellite remote sensing is suitable for observing the widespread forest area in a region because it has a large spatial extent, a relatively high revisit frequency, and stable multi-band observation capabilities [
9]. With the development of high-resolution satellite systems such as Beijing-3 and WorldView, many more observations of forest areas over a large area have been realized. RGB satellite images can be used to get visible-band vegetation indices such as VARI, GLI and ExG [
10]. Although these indicators do not contain near-infrared data, they can still show the health and stress of the canopy to some extent [
11]. Therefore, they offer some reference points for identifying trees damaged by pine wood nematode. At the same time, deep learning has also been used to automatically recognize PWD symptoms [
12]. Deep neural networks can learn discriminative patterns directly from image data, unlike methods based on hand-crafted features, and are generally more suitable for complex forest backgrounds [
13]. Based on the above, this paper will use satellite remote sensing, visible-spectrum vegetation indices and deep learning-based object detection to identify PWD-infected trees automatically [
14].
Most of the deep learning-based object detection methods fall into the two-stage and one-stage frameworks. A two-stage detector generates candidate regions first, and then classifies and regresses bounding boxes [
15]. We design R-CNN-style models, which are good at localizing, as shown above [
16]. However, the multi-step procedure is also computationally expensive and therefore less suitable for time-sensitive applications of remote sensing data. A single-stage detector directly predicts object classes and bounding boxes in one forward pass [
17]. They have a simple inference pipeline and are thus relatively high performance; they are widely used for real-time and large-scale detection tasks [
18]. The YOLO family is a typical case of this development. YOLOv3 used an optimized Darknet backbone and was then applied to PWD detection. YOLOv4 and YOLOv5 enhanced multi-scale feature extraction through BoF/BoS strategies and feature pyramids. YOLOv7 focused more on lightweight inference, and YOLOv8 is an anchor-free design using a C2f-based head to enhance both accuracy and speed [
19]. YOLOv11 has been enhanced with modules such as C3k2 and C2PSA in recent times to improve detection performance further. Although there have been many improvements, CNN-based detectors are still relatively limited in modeling long-range spatial correlations of satellite forest imagery because of the local receptive field nature of convolution. Therefore, transformer-based detectors have recently been introduced [
20]. DETR is an encoder–decoder Transformer that has been introduced to address the problem of manual anchor design and non-maximum suppression in object detection [
21]. RT-DETR has increased the above framework by adding a hybrid encoder and an efficient query selection mechanism to address both convergence issues and the computational cost of the previous DETR-like models [
22]. Among the above architectures, RT-DETR-L combines the HGNetv2 backbone and a Transformer encoder, and is suitable for satellite image analysis that requires both local detail perception and broader contextual understanding. Therefore, RT-DETR-L is chosen as the baseline model for further optimization in this study.
Although some progress has been made in the development of PWD detection models recently, accurately detecting PWD-infected pine trees in satellite remote-sensing images remains challenging. First, many of the available methods are mainly based on pixel-level visual features and do not extensively utilize disease-related prior knowledge. Such knowledge may include alterations in canopy shape during the development of the disease, indicators of plant health, and spatial distributions of disease spread. Without such information, early-infected trees may be missed; especially when the symptoms are mild and the visual difference in a healthy and diseased tree’s canopy is small, they are even harder to spot. Second, although the various spectral information in satellite images can be employed, vegetation indices are often used only as supplementary inputs. They are not always closely related to the spatial texture features, and thus the combined discriminatory power of spectral and visual cues is relatively low. Third, remote sensing data generally contain a larger number of healthy trees than diseased ones. This imbalance may cause the training process to favor the dominant background or healthy samples, reduce the model’s sensitivity to minority diseased targets, and thus lower localization stability [
23]. The above problems are shown in
Figure 1. As shown in
Figure 1a, without disease-specific semantic guidance, infected trees and visually similar healthy backgrounds may have the same colors and textures, thus increasing the risk of confusion.
Figure 1b shows that diseased trees may not be sufficiently distinguishable in the original RGB image, whereas vegetation indices such as VARI, GLI, and ExG provide different responses to canopy damage, indicating that these vegetation-index cues should be effectively fused with RGB spatial features rather than used only as isolated auxiliary information.
Figure 1c also shows that diseased tree crowns occupy only a small proportion of complex remote-sensing scenes as reflected by the bounding-box area-ratio distribution, resulting in a very uneven foreground–background distribution and making minority-target detection more challenging. Together, these examples show that reliable satellite-based PWD detection needs a model with enhanced vegetation-related signal strengthening, integration of disease-relevant semantic information, and retention of fine local target details [
24]. Thus, a research gap has been identified: although there are existing satellite-based PWD detectors, they do not yet have an effective end-to-end mechanism for the joint exploitation of vegetation-index information, domain semantic knowledge, and fine-grained local features. To address the above problem, SGM-RTDETR based on RT-DETR-L is proposed in this paper. SVFM and DFRM are introduced in the proposed framework to enhance feature representation and discrimination ability for diseased target plants in complex forest environments through multi-dimensional clustering design. The objective of this study is to improve the accuracy and robustness of PWD detection in satellite images, expand its application scope, and reduce deployment costs. We hypothesize that integrating vegetation-index enhancement, disease-related semantic guidance, and refined local-detail modeling into RT-DETR-L can improve the discrimination and localization of PWD-infected trees in complex forest scenes.
Given these limitations, we place emphasis on three specific problems in satellite-based PWD detection. First, disease-related prior knowledge needs to be better used. Second, vegetation-index cues should be combined more closely with visual features. Third, weak symptoms must be distinguished more reliably in complex forest scenes. On this basis, RT-DETR-L was adopted as the baseline detector because it provides a favorable balance between accuracy and efficiency. We further developed SGM-RTDETR by combining semantic enhancement with feature refinement. The main contributions are listed below.
(a) A high-resolution satellite remote sensing annotated dataset, named Naro, is constructed specifically for PWD detection. This dataset contains 952 professionally annotated satellite images covering infected pine tree targets against complex forest backgrounds, providing reliable data support and an evaluation benchmark for PWD detection research in satellite remote sensing scenarios.
(b) A Semantic–Visual Fusion Module (SVFM) is proposed. Through vegetation index-guided visual enhancement and Stackelberg game-based visual–textual collaborative fusion, spectral information and domain-specific semantic priors are introduced at the input stage and the decoder input stage, respectively, enabling hierarchical complementary modeling of multi-source information and thereby enhancing the discriminative capability for disease targets under complex backgrounds.
(c) A Disease Feature Refinement Module (DFRM) is proposed. This module operates on the encoder memory feature pathway and further optimizes the SVFM-augmented features through three successive stages: channel recalibration, local detail refinement, and residual enhancement. This design emphasizes channel recalibration in highlighting the more important information about the disease features, channel local refinement in enhancing the depiction of minute lesions and minimal structural differences, and residual improvement in maintaining stability in the transmission of features and retaining valuable original material. Consequently, the model has become more efficient in recognizing and pinpointing more subtle disease patterns in complicated remote sensing scenes.
3. Results
3.1. Experimental Environment and Training Details
To keep the comparisons consistent, all experiments were conducted under the same computing environment and software configuration. The detailed hardware and software specifications are listed in
Table 1. The core training hyperparameters for the current dual-innovation experiment were set according to the final training script train_combined_vi_svfm_rslpo.py as follows: epochs = 100, batch = 4, imgsz = 640, optimizer = AdamW, lr0 =
, lrf = 0.01, momentum = 0.937, weight_decay =
, warmup_epochs = 3, patience = 50, workers = 0, and seed = 42. Automatic mixed precision (AMP) was enabled during training. In this study, workers = 0 means that data were loaded in the main process. This setting was used to maintain a stable and reproducible training environment under the current experimental platform and dataset scale, rather than to indicate an optimal data-loading configuration for larger-scale training scenarios.
For the newly introduced SVFM and DFRM parameters, the training script appends them as an independent optimizer parameter group with a reduced learning rate of , namely . This grouped learning-rate strategy was used to reduce the disturbance of the newly introduced modules to the pre-trained feature distribution during optimization. During training, several data augmentation strategies were used, including HSV color perturbation, random translation, random scaling with scale , random horizontal flipping with , Mosaic augmentation, RandAugment, and random erasing with . Specifically, Mosaic augmentation was applied with a probability of during the first 90 epochs and was disabled during the last 10 epochs to facilitate model convergence. MixUp, CutMix, vertical flipping, shearing, rotation, and perspective transformation were not used.
The CLIP text embeddings used in SVFM were generated using the ViT-B/32 model and were pre-computed and cached for the domain-specific textual descriptions of each training image. Therefore, this text-embedding process introduced no additional text-encoding overhead during inference.
For quantitative and statistical analysis, no additional inferential statistical tests were conducted. Instead, all models were compared under the same dataset split, training configuration, and evaluation protocol using standard object detection metrics, including Precision, Recall, mAP@0.5, and mAP@0.5:0.95. Model complexity and deployment efficiency were further evaluated using Params, GFLOPs, and inference speed.
3.2. Evaluation Metrics
We assess detection performance using four metrics: mAP@0.5, precision, recall, and mAP@0.5:0.95. Their calculation formulas are presented below.
MAP is obtained by averaging AP across all categories. AP represents the area under the precision–recall curve and describes how precision and recall change as the confidence threshold varies. Because of this, mAP is commonly used to reflect the overall detection quality of a model. In our experiments, mAP@0.5 is computed at an IoU threshold of
, whereas mAP@0.5:0.95 is calculated by averaging the results over IoU thresholds from
to
with an interval of
:
Precision measures how accurately the model identifies positive targets. TP (True Positive) in the present research means infected pine trees that have been properly identified while FP (False Positive) refers to healthy pine trees that have been wrongly categorized as infected targets:
Recall indicates the number of infected pine trees that the model can identify correctly. In this research, FN (False Negative) stands for infected pine trees that were wrongly classified as healthy targets:
IoU (Intersection over Union) denotes the ratio between the overlapping area and the union area of a predicted bounding box
and its matched ground-truth bounding box
. It is applied when determining whether a detection result can be considered a true positive:
In the equation above, denotes the predicted bounding box, and denotes the matched ground-truth bounding box. In every comparative experiment conducted in this paper, mAP@0.5 is the main evaluation measure and mAP@0.5:0.95 is a secondary measure so that the findings are consistent with the research carried out by the mainstream in this discipline.
3.3. Model Performance Analysis
In order to examine generalization, we have also considered a five-fold validation scheme based on samples. The data was divided into five subsets of equal size, and in every round, one of them served as a validation set and the remaining four were used to train. It was done until the five subsets were used once as a validation set. On every fold, the best model of that run was chosen and the overall accuracy was given as an average of the five folds.
Figure 4b demonstrates that SGM-RTDETR has similar performance at various data partition settings. The mAP@0.5 values on the five folds are 83.33% (fold 1), 83.22% (fold 2), 82.53% (fold 3), 82.62% (fold 4) and 79.96% (fold 5), which results in an average of 82.33% and a standard deviation of 1.23%. The respective mAP@0.5:0.95 values are 37.77 (fold 1), 36.52 (fold 2), 37.34 (fold 3), 38.76 (fold 4) and 37.00 (fold 5) with the average of 37.48 and the standard deviation of 0.76. Even though the fifth fold is slightly lower than the rest, the variation between the folds is still minimal. It implies that the model has great generalization strength and consistent performance in the case of random sampling.
In order to further test the spatial transferability of the model, we performed representative detection validation on satellite remote sensing images of various site types in Zhangjiajie City. The images were taken in the Yongding District and Cili County of Zhangjiajie City, Hunan Province (
N–
N,
E–
E). This area is characterized by a variety of landscapes, such as dense coniferous forests, sparse mixed forests, farmland, and areas with a mixture of buildings and plants. Nine representative samples of various scene types were chosen for qualitative visual validation, as illustrated in
Figure 4b, where the blue boxes indicate the detection results generated by SGM-RTDETR. It should be noted that
Figure 4b is used to provide representative visual examples rather than an independent quantitative comparison; the quantitative performance of the model is evaluated using the cross-validation results in
Figure 4a and the standard detection metrics reported in the comparative experiments. It can be seen that SGM-RTDETR is able to locate small numbers of targets in sparsely wooded areas, identify diseased pine tree targets in building–vegetation mixed-scene backgrounds, and maintain stable detection behavior in densely wooded areas with larger target populations and highly similar background textures. These findings indicate that the model is likely to have good prospects of being applied in a wide range of pine wilt disease detection settings.
To make the detection results easier to interpret,
Figure 5 displays four representative groups of results arranged by columns. From top to bottom, each row shows the original remote sensing RGB image, the ExG map, the VARI map, the GLI map, and the detection results produced by SGM-RTDETR. Unlike the conventional Normalized Difference Vegetation Index (NDVI), which depends on near-infrared information, this study uses vegetation indices computed only from visible RGB bands, namely the Excess Green Index (ExG), the Visible Atmospherically Resistant Index (VARI), and the Green Leaf Index (GLI). Their calculation formulas are given below:
In these equations,
R,
G and
B represent the pixel values of the red, green and blue channels respectively. The three vegetation-index maps are still spatially registered to the original images so that direct comparison between the model predictions and the spectral responses at the same location is viable. According to
Figure 5, smaller vegetation-index values (especially in warm-colored areas) typically imply greater vegetation stress, degradation or mortality. Most of the detection boxes generated by SGM-RTDETR are found in or close to such low-value areas, indicating that the recognized diseased objects are not only spatially well localized but also align with biologically meaningful stress patterns. In contrast to NDVI, which requires multispectral or hyperspectral images, the RGB-based vegetation indices applied in this paper can be calculated using conventional visible band images only. It reduces the cost of data acquisition and renders the method more feasible to perform large-area PWD studies on satellite systems.
3.4. Module Effectiveness Experiments
Two modules were considered in the presented work, namely, SVFM and DFRM. The assessment started with SVFM which was introduced in the baseline model as first step and followed by the analysis of DFRM in the same environment. In this way, the effect of each module could be observed through their gradual incorporation into SGM-RTDETR.
3.4.1. Effectiveness of the SVFM Module
To assess the contribution of SVFM, we compared it with several widely used fusion approaches, namely simple concatenation (Concat), Feature-wise Linear Modulation (FiLM), and Cross-Attention fusion [
30,
31,
32]. The detailed quantitative comparison results are reported in
Table 2. Experimental results show that the SVFM achieves an mAP@0.5 of 79.71% and an mAP@0.5:0.95 of 35.41% on the test set, outperforming all other compared fusion strategies overall. This indicates that relying solely on simple concatenation or a single interaction mechanism is insufficient to fully exploit the complementary value between visible-band vegetation indices and domain-specific textual semantics, whereas the SVFM, through its hierarchical collaborative design of “input-side VI visual enhancement and decoder input-side textual semantic enhancement”, can more effectively improve the discriminability and robustness of the encoded features [
33].
3.4.2. Effectiveness of the DFRM Module
In
Table 3, to validate the effectiveness of the DFRM module under complex backgrounds and subtle disease feature scenarios, this paper compares it with typical lightweight attention/feature enhancement methods, including SE, CBAM, and ECA [
34,
35,
36]. The results show that the DFRM achieves an mAP@0.5 of 79.70% and an mAP@0.5:0.95 of 35.61% on the test set, outperforming all compared methods. This demonstrates that the hierarchical strategy of jointly performing channel recalibration, nonlinear feature refinement, and residual enhancement on the encoder memory pathway, compared with single-dimensional attention reweighting, can more effectively activate discriminative channel responses relevant to infected tree detection, thereby improving the model’s perception capability for subtle disease regions under complex forest backgrounds.
3.5. Ablation Experiments
In order to analyze the function of each of the proposed modules with respect to detection performance, we incorporated SVFM and DFRM into the RT-DETR baseline one at a time and then assessed the model with both modules applied [
37]. The detailed ablation results are summarized in
Table 4. The unified evaluation setting achieves a score of 78.01% mAP@0.5 and 33.63% mAP@0.5:0.95 using the baseline model. The addition of the SVFM leads to an increase in those values to 79.71% and 35.41% respectively. The respective metrics when using only DFRM are 79.70% and 35.61%. Combining the two modules further enhances the mAP@0.5 to 80.75%, which is the best result across all the configurations, whereas the value of mAP@0.5:0.95 becomes 35.43%. The findings indicate that SVFM and DFRM are supplementary to each other in enhancing the main detection indicator. Although the dual-module model does not surpass all the single-module settings on mAP@0.5:0.95, it yields the highest mAP@0.5, which better matches the practicality of the primary detection capability in the real-life problem of identifying diseases.
The findings indicate that either SVFM or DFRM can enhance the performance of RT-DETR baseline when implemented independently, but the improvement is not the same. The SVFM-only model achieves 79.71 percent mAP@0.5, and the DFRM-only model achieves 79.70 percent, both greater than the baseline value of 78.01. Combining the two modules causes mAP@0.5 to increase even further, up to 80.75, which is the highest across all configurations. Such a pattern suggests that the two improvement methods can be applied complementarily and they do their job well to enhance the detection of infected trees in complex scene conditions.
The joint model is not the best-performing model on all evaluation metric, and its mAP@0.5:0.95, precision and recall are not always greater than those of the single module variants, though the gaps tend to be minimal in general. It indicates that the greatest benefit of integrating the two modules is enhancing the overall quality of detection instead of maximizing the value of all other secondary measures simultaneously. With the combination of the previous data optimization technique, the optimized training samples offer a better foundation to deal with complex backgrounds, variations in target scales as well as subtle texture differences. In such situations, SVFM can make a greater contribution to semantically enhance, whereas DFRM can make a more effective contribution to locally refine details. The combined effects of both modules are quite complementary: the model exhibits the highest improvement in mAP@0.5 and is relatively stable across the rest of the evaluation metrics, which confirms the utility of the approach to identify PWD-affected trees.
3.6. Comparison with State-of-the-Art Methods
3.6.1. SGM-RTDETR Performance on Naro Dataset
SGM-RTDETR was compared with seven representative detectors under the same test conditions, including YOLOv3, YOLOv5s, YOLOv8n, YOLOv9c, YOLOv10n, YOLOv11n, and RT-DETR-L. The quantitative results are summarized in
Table 5. Compared with the lightweight YOLO-series models, SGM-RTDETR achieved the highest mAP@0.5 of 0.8074 and a competitive mAP@0.5:0.95 of 0.3543, while maintaining moderate model complexity with 31.987 M parameters, 102.49 GFLOPs, and 30.00 FPS. YOLOv11n had a shorter inference time, but its mAP@0.5 was still lower than that of SGM-RTDETR. SGM-RTDETR has improved the mAP@0.5 of RT-DETR-L without increasing the number of parameters or computational cost significantly. Thus, the new model is more suitable for the trade-off between detection accuracy and runtime speed in PWD recognition on satellite images.
Figure 6 shows the detection results of all models on some representative images in the Naro test set. The six examples chosen were designed to be relatively difficult, with some weak symptoms, small targets, a cluttered forest background, road-forest mixing, and dense candidate regions. The results of some of the baseline models still have missed detections, repeated predictions, unstable confidence scores, or false alarms due to background interference. SGM-RTDETR performs better in the above cases; it has a more stable result, clearer localization, and consistent detection responses. The two are likely related to the function of SVFM and DFRM. SVFM strengthens disease-related feature discrimination by integrating visible-band vegetation cues and CLIP-based text semantics. DFRM then refines the decoder features through channel recalibration and residual enhancement. Overall, both the metric results and the visual comparisons indicate that SGM-RTDETR can better identify PWD-related targets in complex satellite scenes.
3.6.2. Performance of SGM-RTDETR on the Roboflow Dataset
To further assess the performance and generalization of SGM-RTDETR, we used a publicly available PWD detection dataset from the Roboflow platform
https://universe.roboflow.com/project-dkq3q/-9pmdt/dataset/8 (accessed on 19 February 2026) [
38]. The original dataset contains 4301 training images, including brightness augmentation ranging from
to
, together with 412 validation images and 202 test images, all at a resolution of
pixels. To keep the experimental scale manageable while examining how the model generalizes under limited training data, we selected 800 images from the original training set to form a training subset, whereas the validation and test sets were kept unchanged. We screened the images in this dataset and compared SGM-RTDETR against six existing detection methods under identical experimental conditions.
Table 6 shows that SGM-RTDETR delivers the strongest performance on the public PWD dataset among the compared methods. Its mAP@0.5 reaches 83.3%, which is 3.9 percentage points higher than RT-DETR (79.4%) and 0.7 points above YOLOv8n (82.6%), the second-best model. The model also records 80.2% precision, representing a 2.1-point gain over the RT-DETR baseline. Recall reaches 77.6%, which is 0.8 points higher than the baseline. The overall results on the public dataset suggest that the method is good at generalizing and still has a significant improvement over RT-DETR in mAP@0.5.
The performance benefits of SGM-RTDETR on the PWD dataset are due to such factors as: (a) the fact that SGM-RTDETR is based on the RT-DETR architecture and inherits the benefits of the Transformer encoder–decoder structure in the global feature modeling, which allows the better capturing of the global contextual relationship between the PWD-infected areas and the healthy vegetation around them; (b) the Semantic–Visual Fusion Module (SVFM) that is based on the Stackelberg game, through the integration of CLIP textual semantics information, increases the semantic comprehension of the model to the PWD features, allowing the more precise distinction between dead trees of pine and other visually alike land cover features (bare soil, dead branches, etc.); (c) the vegetation indices (ExG, VARI, GLI), which are based on RGB, act as additional input sources, offering the model a direct quantitative insight into the vegetation health state, making up the lack of vegetation stress recognition ability of pure RGB images; and (d) the optimization strategy of DFRM, i.e., random subgroup selection and adaptive feature refinement, improves the learning ability of the model in relation to hard samples during training, thus increasing the strength of the detection. All these findings indicate that SGM-RTDETR does not only perform well in the self-constructed dataset but also on the public dataset, which suggests that the given approach can be considered effective and generalizable.
3.6.3. Performance of SGM-RTDETR on the PDT Dataset
To further evaluate the cross-dataset generalization ability of SGM-RTDETR, we introduced the publicly released PDT dataset from the PDT_CWC_YOLO-DP project
https://github.com/RuiXing123/PDT_CWC_YOLO-DP (accessed on 27 May 2026). According to the dataset authors, the PDT dataset is the first high-precision UAV dataset specifically designed for the targeted detection of tree pests and diseases, and it was collected in real operational environments to fill the gap of dedicated datasets in this field. Compared with satellite remote sensing imagery, UAV-acquired imagery has different imaging perspectives, target scales, and background distributions [
39]. Therefore, evaluation on the PDT dataset provides an additional cross-source and cross-platform test for the proposed method. The original PDT dataset contains 4301 training images, 412 validation images, and 202 test images. Under identical training and evaluation settings, SGM-RTDETR was compared with seven existing detectors.
Table 7 shows that SGM-RTDETR achieves the best overall performance on the PDT dataset among the compared methods. Its mAP@0.5 reaches 79.81%, which is 2.55 percentage points higher than RT-DETR (77.26%) and 0.94 points higher than YOLOv11n (78.87%), the second-best model in this metric. SGM-RTDETR achieves the highest precision of 80.79% and recall of 79.64%, and thus can detect tree disease targets in UAV images with a relatively high degree of both accuracy and sensitivity. Its mAP@0.5:0.95 is not the highest among all models, but it is still 2.61 percentage points better than RT-DETR. These results indicate that SGM-RTDETR can maintain competitive performance on an independent public UAV dataset and shows robustness to variations in image sources and acquisition conditions.
The PDT results show that the following parts help improve SGM-RTDETR: global context modelling, semantic-guided feature enhancement, vegetation-index cues and adaptive decoder refinement. SGM-RTDETR is not only for using RGB images but also incorporates both semantic information and vegetation-related responses in its disease identification of trees in complex UAV images. The PDT experiment further shows that the model can transfer to data beyond the self-constructed Naro dataset and the existing Roboflow PWD dataset.
4. Discussion
The three problems in the existing detectors of satellite-based detection of pine wilt disease (PWD) were addressed in this study to improve them. First, the disease-related semantic knowledge is not utilized. Second, visible-band vegetation cues are often only weakly combined. Third, the specific traits of the disease are still hard to express. Based on the previous studies of forest disease monitoring and remote sensing object detection, spectral changes, background contexts, and object-level spatial characteristics can all serve as indicators of early-stage or minor symptoms of vegetation stress. Many general-purpose detectors have only learned from RGB images thus far. Therefore, if the symptoms of PWD are mild, the diseased areas are small, or the surrounding forest environment is complex, it may not be suitable for this method. To address the above problems, we design SGM-RTDETR within the RT-DETR framework by integrating vegetation-index-enhanced visual cues, CLIP-based semantic guidance and feature refinement.
As shown in
Figure 7b, SGM-RTDETR achieved an mAP@0.5 of 80.75% under the same experimental conditions, and it was higher than the 78.01% obtained by RT-DETR-L. Therefore, it is proposed that a two-module design will be used to recognise diseased pine crowns. In accordance with the above research results, auxiliary information at the domain level can enhance the precision of remote sensing detection models. SVFM adds improvements to vegetation indices and text-based semantic information in our framework as additional cues for distinguishing PWD-affected crowns from complex backgrounds. DFRM strengthens the representation of local texture and structural variations in the memory feature extraction stage of the decoder. The two modules are not the same but work together. SVFM expands semantic–visual discrimination, and DFRM increases feature consistency for local stabilization.
Figure 7a shows some more typical examples. SGM-RTDETR performs better in areas with mild disease symptoms, small infected crowns, a mixed forest-road-building background, and a high density of candidate objects. The above visual observations are consistent with the numerical results, and it can be concluded that the new modules improve the accuracy of detection in complicated satellite images. Detection based only on RGB appearance is not sufficient; therefore, visible-band vegetation indices that contain information about canopy color variation and thus are related to PWD symptoms, such as VARI, GLI, and ExG, should also be added. At the same time, text-guided semantic information helps the model pay more attention to disease-related visual patterns and is no longer solely based on low-level appearance features. Based on previous research, the above results suggest that domain knowledge and semantic guidance can be used to improve forest disease detection in remote sensing images.
The experiments also have some deficiencies. As shown in
Table 5, SGM-RTDETR reached 35.43% for mAP@0.5:0.95, but it was not the highest among all the other methods. Therefore, it can be seen that localization accuracy at a high IoU threshold has not improved yet. SVFM and DFRM are likely to improve semantic separation and general detection stability, but they do not specifically address the problem of bounding box regression. In other words, the current model gives more weight to target recognition and has not yet strengthened precise box localization sufficiently. Another problem is that, at present, the way it works is based only on RGB images and the visible-band vegetation indices derived from them. In actual forest conditions, the cause of canopy change may be PWD; however, other reasons such as drought, shade, variations in tree species, seasonal changes and other disturbances can also lead to such a change. Therefore, under certain field conditions, the model may still misclassify infected trees as healthy or stressed. This limitation should therefore be considered when the model is applied to operational forest monitoring.
Future work will focus on several improvements. First, a bounding-box refinement module can be added to improve the accuracy of localization, such as cascade regression or deformable convolution. Second, the loss function can be modified to increase the penalty weight for high-IoU regions and thus improve the accuracy of box prediction. Thirdly, the semantic information generated by SVFM could be more closely coupled with the bounding-box regression branch to provide semantic priors for both classification and localization. Future studies should also incorporate near-infrared or multispectral imagery rather than relying only on RGB data, and these extra spectral bands will be used to find more reliable cues for distinguishing PWD-related stress from non-disease stress compared to just RGB data. Multi-scale feature fusion also needs to be improved, and the location of disease in different sizes should also be enhanced.
Overall, SGM-RTDETR shows that semantic–visual fusion and decoder feature refinement can improve PWD target recognition in satellite imagery without greatly increasing model complexity. The framework still needs further improvement in high-IoU localization and generalization across multiple data sources. Even so, it shows practical potential for large-scale forest disease screening. Therefore, SGM-RTDETR is more suitable as an auxiliary tool for remote sensing-based early warning and monitoring of PWD, rather than as an independent or final basis for field diagnosis.