2D and 3D Urban Change Detection Methods Using Remote Sensing: A Review
Highlights
- This review highlights a clear shift from conventional pixel-based and object-based methods to learning-based approaches. Traditional techniques struggle with high-resolution data and complex feature representation. In contrast, deep learning models, especially CNNs and autoencoders, effectively capture hierarchical and nonlinear features, leading to more accurate real-world representations.
- 2D data is effective for detecting horizontal changes such as land cover and building footprints, while 3D data provides essential information on vertical and volumetric changes like building height. However, deep learning for 3D change detection is still in its early stages compared to 2D approaches. It also faces key challenges, including high data acquisition costs, noise in 3D data, and the need for high-performance computing resources.
- Continuous and precise monitoring of building dynamics through these advanced methods is essential for informed decision making in urban planning, sustainable development, and smart city management.
- To overcome current limitations, the sources suggest that future research must focus on developing lightweight models and label-efficient learning strategies (such as self-supervised or synthetic data) to reduce the heavy reliance on massive, labeled datasets and high computational power.
Abstract
1. Introduction
2. Background
3. Urban Change Detection Pattern and Publications
3.1. Dataset Definition and Search Strategy
3.2. Publication Trends
3.3. Keyword Co-Occurrence Analysis
3.4. Highly Cited Papers and Method Categories
3.5. Method Evolution and Summary
4. Review and Classification of Change Detection Methods
4.1. 2D Change Detection Methods
4.1.1. Conventional 2D Change Detection Methods
4.1.2. Learning-Based 2D Change Detection Methods
CNNs in 2D Change Detection
AEs in 2D Change Detection
RNNs in 2D Change Detection
GANs in 2D Change Detection
DBNs in 2D Change Detection
4.2. 3D Change Detection
4.2.1. Conventional 3D Change Detection Methods
Geometric Comparison
Geometric Spectral Analysis
4.2.2. Learning-Based 3D Change Detection
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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| Title | Authors | Year | Cites | Method Category | DOI |
|---|---|---|---|---|---|
| Change detection techniques | Lu, D. et al. | 2004 | 2200 | Review | 10.1080/0143116031000139863 [11] |
| A Spatial-Temporal Attention-Based Method and a New Dataset for Remote Sensing Image Change Detection | Chen, H et al. | 2020 | 1549 | 2D Deep Learning Change Detection | 10.3390/rs12101662 [14] |
| UNetFormer: A UNet-like transformer for efficient semantic segmentation of remote sensing urban scene imagery | Wang, L.B. et al. | 2022 | 1008 | 2D Deep Learning Change Detection | 10.1016/j.isprsjprs.2022.06.008 [15] |
| DASNet: Dual Attentive Fully Convolutional Siamese Networks for Change Detection in High-Resolution Satellite Images | Chen, J. et al. | 2021 | 575 | 2D Deep Learning Change Detection | 10.1109/JSTARS.2020.3037893 [16] |
| Building Change Detection for Remote Sensing Images Using a Dual-Task Constrained Deep Siamese Convolutional Network Model | Liu, Y. et al | 2021 | 537 | 2D Deep Learning Change Detection | 10.1109/LGRS.2020.2988032 [17] |
| SwinSUNet: Pure Transformer Network for Remote Sensing Image Change Detection | Zhang, C. et al. | 2022 | 511 | 2D Deep Learning Change Detection | 10.1109/TGRS.2022.3160007 [18] |
| Change Detection Based on Artificial Intelligence: State-of-the-Art and Challenges | Shi, W.Z. et al. | 2020 | 492 | Review | 10.3390/rs12101688 [12] |
| SemiCDNet: A Semi supervised Convolutional Neural Network for Change Detection in High Resolution Remote-Sensing Images | Peng, D.F. et al. | 2021 | 364 | 2D Deep Learning Change Detection | 10.1109/TGRS.2020.3011913 [19] |
| Change Detection on Remote Sensing Images Using Dual-Branch Multilevel Intertemporal Network | Feng, Y.C. et al. | 2023 | 360 | 2D Deep Learning Change Detection | 10.1109/TGRS.2023.3241257 [20] |
| URBAN CHANGE DETECTION FOR MULTISPECTRAL EARTH OBSERVATION USING CONVOLUTIONAL NEURAL NETWORKS | Daudt, R.C. et al. | 2018 | 354 | 2D Deep Learning Change Detection | 10.1109/IGARSS.2018.8518015 [21] |
| Urban land-cover change detection through sub-pixel imperviousness mapping using remotely sensed data | Yang, L.M. et al. | 2003 | 233 | 2D Traditional Change Detection | 10.14358/PERS.69.9.1003 [22] |
| SFEARNet: A Network Combining Semantic Flow and Edge-Aware Refinement for Highly Efficient Remote Sensing Image Change Detection | Li, M. et al. | 2025 | 232 | 2D Deep Learning Change Detection | 10.1109/TGRS.2025.3545906 [23] |
| 3D change detection—Approaches and applications | Qin, R. et al. | 2016 | 230 | Review | 10.1016/j.isprsjprs.2016.09.013 [13] |
| Spatiotemporal Enhancement and Interlevel Fusion Network for Remote Sensing Images Change Detection | Huang, Y.Y. et al. | 2024 | 221 | 2D Deep Learning Change Detection | 10.1109/TGRS.2024.3360516 [24] |
| PGA-SiamNet: Pyramid Feature-Based Attention-Guided Siamese Network for Remote Sensing Ortho imagery Building Change Detection | Jiang, H.W. et al. | 2020 | 218 | 2D Deep Learning Change Detection | 10.3390/rs12030484 [25] |
| Change Detection from Very-High-Spatial-Resolution Optical Remote Sensing Images: Methods, applications, and future directions | Wen, D.W. et al. | 2021 | 205 | 2D Traditional Change Detection | 10.1109/MGRS.2021.3063465 [26] |
| Adversarial Instance Augmentation for Building Change Detection in Remote Sensing Images | Chen, H. et al. | 2022 | 193 | 2D Deep Learning Change Detection | 10.1109/TGRS.2021.3066802 [27] |
| Building Change Detection in Multitemporal Very High-Resolution SAR Images | Marin, C. et al. | 2015 | 190 | 2D Traditional Change Detection | 10.1109/TGRS.2014.2363548 [28] |
| Building Change Detection from Multitemporal High-Resolution Remotely Sensed Images Based on a Morphological Building Index | Huang, X. et al. | 2014 | 190 | 2D Traditional Change Detection | 10.1109/JSTARS.2013.2252423 [29] |
| Method Evolution Stage | 2D Traditional Change Detection | 2D Object-Based Change Detection | 2D Deep Learning Change Detection | 3D Traditional Change Detection | 3D Deep Learning Change Detection | Review | Total |
|---|---|---|---|---|---|---|---|
| 2000–2009 Early traditional stage | 22 (66.67%) | 2 (6.06%) | 0 (0.0%) | 2 (6.06%) | 0 (0.0%) | 7 (21.21%) | 33 |
| 2010–2016 Object-based and 3D growing stage | 61 (53.98%) | 8 (7.08%) | 2 (1.77%) | 29 (25.66%) | 0 (0.0%) | 13 (11.5%) | 113 |
| 2017–2020 Deep learning emerging stage | 44 (37.61%) | 9 (7.69%) | 31 (26.5%) | 18 (15.38%) | 2 (1.71%) | 13 (11.11%) | 117 |
| 2021–2025 Deep learning and 3D-aware stage | 95 (20.13%) | 10 (2.12%) | 287 (60.81%) | 26 (5.51%) | 16 (3.39%) | 38 (8.05%) | 472 |
| Methodology | Category | Definition | Type of Classification | Advantages | Limitations | Applications |
|---|---|---|---|---|---|---|
| Observation analysis | - | Changes are mapped using direct observations | Supervised | Accurate results | Time-consuming and expensive at large scales and difficult map updating | Various applications before object- and pixel-based conventional methods [43] |
| Mathematical computation-based methods | Image difference | Changes are mapped using mathematical computations or transformations | Unsupervised | Simple and practical, easy visualization, reduced effects of solar radiation on images and shadows in topography | Challenge in effective thresholding to generate the final change map, difficulties in setting effective bands for each method, inability to generate multiple final change maps, and non-normal output distribution | Land use, urban, and urban cover changes [31,43] |
| Image regression | ||||||
| Image ratio | ||||||
| Change vector analysis | ||||||
| Vegetation index difference | ||||||
| Transformation-based methods | PCA | Changes are mapped using a transformation. These methods generate change maps using a correlation and variance between images. | Unsupervised | Emphasis on information differences | Data of the change details cannot be extracted | Changes in rural and urban land cover [35], land cover changes [36] |
| Tasseled cap transformation | ||||||
| Chi-square transformation | ||||||
| Gram–Schmidt transformation | ||||||
| Classification-based methods | Post-classification methods | Changes are mapped using a classification technique | Supervised Unsupervised Hybrid | A change information matrix is obtained, and no atmospheric correction is required | Challenging selection of training data | Land cover changes [37], urban land cover changes [35,37], forested land changes [40] |
| Spectral and spatial feature combination analysis | ||||||
| Expectation-maximization analysis | ||||||
| Unsupervised change detection methods | ||||||
| Hybrid methods | ||||||
| Artificial neural networks | ||||||
| Advanced methods | Li–Strahler reflectance model | Spectral reflectance is converted into physical parameters | Hybrid | Effective for comparison of the spectral signatures of images. They can extract vegetation information | Complex and time-consuming procedure. It is challenging to develop such methods | Land cover changes [43] |
| Spectral combination models | ||||||
| Biophysical parameter-based models | ||||||
| GIS-based methods | Coupled GIS–remote sensing methods | Use of various database sources for change detection | Hybrid | User information is updated directly through the GIS database | Change map quality is dependent on the type of data | Forest change detection [31] |
| GIS techniques |
| Network | Function | Reference (Introduction) | Reference (Change Detection) | Advantages | Limitations |
|---|---|---|---|---|---|
| CNN | Processing data with a network structure | LeCun et al. [46] | Iino et al. [47] | Hierarchical representation, noise tolerance, and parameter sharing | Low preprocessing, flexibility, and interpretability, and high computational time and cost |
| AE/SAE | Automatic encoding as the main structure | Hinton and Salakhutdinov [48] | Chen et al. [49] | Regeneration, scalability, and noise tolerance | Challenging hyperparameter selection and difficult learning process |
| RNN | Processing sequential data and edge fusion | Bengio et al. [50] | Lyu et al. [51] | Hierarchical data processing and memory element | Overfitting, non-parallel network, and computational complexity |
| GAN | Generating new data with similar statistics to the original data | Goodfellow et al. [52] | Gong et al. [53] | Data generation for unsupervised learning | Difficult training, high parameter sensitivity, and high computational complexity |
| DBN | RBM-based design | Hinton et al. [54] | Argyridis and Argialas [55] | Scalability, transfer learning, and unsupervised learning | High computational complexity, limited to predefined layers, and difficult training |
| Model | Description | Training | Data | Advantage | Limitation | Application | Performance Metrics |
|---|---|---|---|---|---|---|---|
| CNN | Siamese CNN | Supervised | OSCD | Fully connected layer training | Large training dataset | Urban land use changes [56] | Global precision = 96.05 |
| CNN | Simultaneous training of spectral and spatial features | Supervised | Multispectral Taizhou and Kushan image datasets | High performance | Large training dataset | Urban land use changes [57] | Taizhou OA = 98.75, KC = 0.96; Kushan OA = 99.0, KC = 0.98 |
| CNN | Siamese design with a hybrid feature extraction module | Supervised | Multispectral ZY-3 and GF-2 images | Effective deep feature extraction | Lack of efficiency in separating pixels from their adjacencies in classification | Urban and rural land use changes [58] | ZY-3 OA = 97.15, KC = 0.78; GF-2 OA = 94.68, KC = 0.73 |
| CNN | Linear CNN | Supervised | Multispectral Landsat-8 images | End-to-end training | Challenging generation of labeled data | Water body and river changes [59] | KC = 0.79 |
| CNN | Multidimensional CNN | Unsupervised | OSCD | End-to-end | Time-consuming training | Urban cover and land use changes [92] | OA = 98.89, KC = 0.92 |
| CNN | CNN to extract difference features | Pre-trained | Multispectral WorldView-3, QuickBird, and Ziyuan-3 images | Generalizable for various datasets and robust design | Need for large training datasets | Urban land use changes [60] | WorldView-3 KC = 0.61; QuickBird KC = 0.57; Ziyuan-3 KC = 0.5 |
| CNN | Deep Siamese CNN for segmentation | Supervised | RGB images of buildings | Moderated training dataset challenge | Poor performance in detecting the exact building boundaries | Urban construction [61] | AC = 95.24 |
| CNN | Semi-supervised Siamese CNN based on transfer learning | Pre-trained | QuickBird images of the 2010 Haiti earthquake | Reduced computational cost | Mapping errors | Land cover changes [62] | KC = 0.82 |
| CNN | Attention mechanism-based CNN | Supervised | Multispectral LEVID-CD dataset [58] | High performance | Complex design | Urban cover changes [63] | Precision = 91.20, KC = 0.88 |
| CNN | Attention mechanism-based feature fusion network | Supervised | LEVID-CD [58] and WHUCD [59] datasets | Improved feature extraction and fusion | Numerous parameters | Building change detection [64] | LEVID-CD OA = 98.7, KC = 0.89; WHUCD OA = 99.4, KC0.92 |
| CNN | Comparison of CNN-based and Transformer-based models | Supervised Unsupervised Semi-supervised | Hyperspectral, SAR | Effective and accurate feature extraction | CNN: global feature modeling challenge; Transformer: high computational complexity | Multimodal application [65] | Hyperspectral and SAR based on methods OA above 95 and KC above 0.77, respectively |
| CNN, Mamba | Comparison of CNN, Transformer-based, and Mamba learning based frameworks | Supervised Unsupervised Semi-supervised | Multiespectral, SAR, hyperspectral, 3D datastes, LEVIR-CD, WHU-CD | Hybrid models enable pixel- and region-based detection; strong performance | Requires large, labeled datasets | Urban development, disaster assessment [1] | Hyperspectral OA > 95, KC > 0.51; LEVIR-CD OA > 97, precision > 71; WHU-CD OA > 98, Precision > 83 |
| CNN GAN | Comparison of multiple CD methods (HRNet, SLC-CNN, etc.) | Supervised Unsupervised Synthetic | Satellite images | Robust feature extraction; data integration; misclassification handling | High computational cost; large data requirement | Environmental shift, city growth [66] | All data fusion precision = 93.09 |
| CNN RNN GAN Mamba | Comparison of DL models since 2018 | Supervised | High-resolution image, SAR, multispectral, hyperspectral | Strong local/global feature extraction; time-series capability | Class imbalance; multimodal fusion challenges | Environmental and urban transformation [67] | |
| CD-Lamba, CNN, SSM (Mamba) | Introduction and comparison of CD-Lamba | Supervised | Satellite images | Superior performance over Transformer and SSM models | Difficulty distinguishing real vs. pseudo changes | Urban expansion, deforestation, land use changes [68] | OA = 99.32 |
| CNN | Classification into feature-, patch-, image-based models | Self-supervised | Optical remote sensing data | Reduces need for labeled data | Data fusion challenges; costly pixel-level labeling | Urban change detection [69] | OA = 99.75 |
| CNN GAN RNN | Comparison using benchmark datasets | Supervised | OSCD, LEVIR, WHU | High accuracy across changes types | Requires large, labeled datasets | Urban change detection [4] | OSCD OA = 95.8; LEVIR OA = 99.16; WHU OA = 99.64 |
| CNN | LMCNet | Supervised | RMSCOCO | Low number of parameters, lightweight network, suitable performance for multiclass problem | Performance is weaker compared to heavy-weight networks; ablation study shows strong dependency on L2 loss and ghost attention module | Multiclass object counting [70] | MSEA = 39.1 |
| CNN | MSRIHL-CNN | Supervised | Chinese Gaofen-3 SAR data | Effective feature extraction from input image; suitable when labeled data is limited | Requires long training time; sensitive to small targets | Object detection [71] | Recall = 97.39 |
| CNN | MKSFF-CNN | Supervised | SAR images | Suitable classification accuracy; computationally efficient | Requires high training time; sensitive to kernel size | Classification [72] | OA = 97.44 |
| AE | Multispectral Unet | Supervised | OSCD | End-to-end | Low performance | Land use detection [30] | KC = 0.91 |
| AE & RNN | Coupled Unet-LSTM model | Supervised | OSCD | End-to-end | Numerous training data samples | Land use change detection [73] | OA = 96.0 |
| AE | Unet | Supervised | Multispectral KompSAT-3 images | Spectral destruction challenge resolved | Complex computations | Land use and forest change detection [74] | KC = 0.61 |
| AE | Siamese neural network | Supervised | Multispectral Google Earth images in various seasons | End-to-end | Complex model | Urban land use detection [75] | OA = 98.39 |
| AE | Developed Unet and SeNet | Supervised | Multispectral IKONOS images of Wuhan | End-to-end | Large training dataset | 2D and 3D building change detection [76] | OA = 99.46 |
| AE | Attention-based network | Supervised | LEVIR-CD | Effective deep feature extraction | Time-consuming training | Building change detection [77] | OA = 98.95, KC = 0.88 |
| AE | Hierarchical synergy of the Laplacian pyramid | Supervised | High-res satellite images | Deep feature extraction | Complex model | Urban land use detection [30] | OA = 96.73 |
| AE | Features using the DeepLab mask | Supervised | LEVIR-CD and GF-1 images | End-to-end | Ineffective edge detection | Building change detection [78] | LEVIR-CD KC = 0.93, Precision = 98.1; GF-1 KC = 0.68 precision = 94.1 |
| AE | Boundary-aware Siamese neural network | Supervised | LEVIR-CD | End-to-end boundary detection | Complex model | Urban land use [79] | F1-score = 90.78 |
| AE | Efficient Unet+ | Supervised | LEVIR-CD dataset [60] | Fewer computational parameters | Time-consuming model | Land use detection [80] | OA = 85.68 |
| AE | L-Unet | Supervised | OSCD | Coping with the lighting challenge and registration error | Poor performance in preserving object shapes | Urban change detection [81] | Precision = 90 |
| AE | Unet | Supervised | OSCD | Simple model and simple execution | Inefficiency in detecting minor changes | Urban change detection [82] | Balanced Accuracy = 80.57 |
| AE GAN CNN | Comparison including U-Net and SAM for land cover change detection | Supervised Unsupervised Semi-supervised | Optical, RADAR | Good accuracy and performance | Requires large, labeled datasets; sensitive to noise | Land cover change detection [3] | Not reported |
| AE CNN RNN | Comparison of learning methods for DL models | Supervised Semi-supervised Weakly supervised | Satellite datasets (OSCD, LEVIR, WHU) | Strong spatiotemporal feature extraction | Large, labeled datasets; imbalance; multisource challenges | Urban change detection [83] | Precision = 94.3 |
| RNN | RNN | Supervised | Multispectral Taizhou dataset | End-to-end | Inefficiency in extracting all deep features | Urban change detection [84] | OA = 98.04, KC = 0.92 |
| RNN CNN GAN AE | Comparison of DL models for change detection | Supervised | SAR, hyperspectral | High-level feature extraction and accurate detection | High computational cost; complex and time-consuming training | Global and regional variation [85] | OA = 99.19 |
| GAN | GAN | Supervised | Multispectral WorldView-2 and GF1 images | Reduced training dataset | Complex model | Urban and watershed change detection [86] | WorldView-2 OA = 95.01, KC = 0.79; GF1 OA = 96.97, KC = 0.81 |
| GAN | GAN coupled with improved DeepLabV3+ | Unsupervised | OSCD, Landsat-8, and Google Earth images | High performance | Large training dataset | Urban change detection [87] | OSCD OA = 83.6, KC = 0.44; Landsat-8 OA = 96.4 KC = 0.56; Google Earth OA = 91.2, KC = 0.66 |
| GAN | Self-supervised cGAN | Semi-supervised | WorldView-3 images | Extraction of features with multiple spatial resolutions | Complex model | Urban change detection [88] | OA = 84.82 |
| GAN | Dual feature extraction | Supervised | LEVIR-CD and WHUCD datasets | Coping with variation challenges | Parameters α and β | Building change detection [89] | LEVIR-CD precision = 89.4; WHUCD precision = 83.08 |
| DBN | Deep segmentation | Unsupervised | Multispectral Sentinel-2 and Pleiades images | No need for labeling all data | Time-consuming model | Urban change detection [90] | Sentinel-2 OA = 85.62; Pleiades OA = 97.15 |
| DBN | CNN coupled with DBN | Unsupervised | Multispectral SPOT-5, Landsat, and Google Earth images | High accuracy | Time-consuming processing | Urban land use and vegetation changes [91] | Multispectral SPOT-5 OA = 96.77, KC= 0.76; Landsat OA = 96.11, KC = 0.79; Google Earth images OA = 99.84, KC = 0.99 |
| Method | Group | Description | Advantage | Limitation |
|---|---|---|---|---|
| Geometric comparison | Height differencing | Differencing two co-registered DSMs | Simple execution and large-scale practicality | Output sensitivity to data co-registration and image matching errors and practicality for merely 2.5D surfaces |
| Euclidean distance height differencing | Calculating the Euclidean distance between two 3D surfaces | Robust under small registration and full 3D data comparison | Time-consuming computations and complex implementation | |
| Projection-based difference | Calculating the correlation between two 3D data samples and comparing the change | Preventing stereo image matching errors and accuracy and practicality for 3D data of high accuracy | Change detection errors in homogenous areas and the dependence of change map accuracy on input 3D data accuracy | |
| Geometric spectral analysis | Post-refinement | Geometric comparison results are improved using spectral and geometric information | Flexible and relatively effective algorithms and comprehensible and easily executable parameters in the algorithms | Output dependence on geometric comparison and the impossibility of correcting the lost changes in the next steps |
| Direct feature fusion | Geometric and spectral features are fused to detect the changes | A combination of geometric and radiometric data and simultaneous use of various information bands without any need for algorithm improvement | Setting effective fusion parameters remains a major challenge | |
| Post-classification | Object detection or classification is performed, and changes are detected through an analysis | Improved accuracy in object classification and detection | Dependence of output accuracy on classification accuracy and the need for accurate sample collection and feature design |
| Model | Description | Training | Data | Advantage | Limitation | Application | Performance Metrics |
|---|---|---|---|---|---|---|---|
| CNN | Connected component analysis, post-processing, and deep learning network were used. Structural and spectral features were integrated | supervised | Airborne laser scanning and photogrammetric point clouds | Ability to integrate data from multiple sources, extraction of suitable features for building change detection, ability to detect all changes | Errors in FN and FP, sensitivity to vegetation areas, terrain changes and low-quality data, challenges at building boundaries, unbalanced data and overfitting | Building change detection [113] | Recall = 82.40% |
| CNN | CNN network and graph cut algorithm used, with post-processing | supervised | 3D point cloud dense aerial image matching | Errors minimized using co-segmentation, effective feature integration, generalized method for different 3D data, handling occlusion in building areas and small changes | Final error depends on DTM generation error, complexity in urban areas | Building change detection [93] | Completeness = 96.8% |
| CNN | CNN with dual thresholding scheme and post-processing filters | supervised | 3D point clouds | Robust to environmental changes, applied threshold is stable | Computationally expensive, sensitive to complex urban structures, difficulty in detecting small objects | Structural change detection in urban areas [114] | mIOU = 61.3.7% |
| AE | U-Net used for segmentation, improved with morphological operators, multi-class change detection | supervised | 3D LiDAR point clouds | Lightweight model, capable of handling large 3D data, detects multiclass 3D changes | Difficulty in detecting small changes, sensitive to data density | 3D building change detection in urban area [115] | IOU = 86.7% |
| CNN | Feature pyramid network with CNN (5 convolution layers) | supervised | Point clouds from image and DSM | Multiscale feature extraction, handling class imbalance, data fusion | Dependent on preprocessing, requires further improvement | Building change detection [116] | OA = 97.1% |
| GAN | GAN and U-Net with Transformer blocks | supervised | LiDAR point clouds | Efficient and fast, good generalization | Occlusion and shadow artifacts in complex areas | Binary change detection urban street [117] | IOU = 62% |
| CNN | Siamese network with kernel point convolution | supervised | LiDAR point clouds | Use of raw data, one-stage change detection | Computational complexity, limited to binary changes, geometric ambiguity in roofs | Urban change detection [118] | mIOU = 93.27% |
| CNN | Combined 2D image features and 3D point cloud features for multiclass detection | supervised | Point cloud from stereo image matching | Integration of 2D and 3D features, high automation, improved boundary extraction | Computational complexity, challenges with tall/complex buildings and small objects | Building change detection [10] | OA = 99.0% |
| CNN | Change detection using single-time DSM | supervised | LiDAR point clouds | Reduced need for bi-temporal data, efficient feature learning, noise reduction | Lower accuracy compared to bi-temporal data, dependency on training dataset | 3D urban change detection [119] | Kappa = 0.679 |
| CNN GAN RNN | Comparison of 3D data using different networks | supervised | Point clouds | 3D data not affected by environmental conditions | High cost of 3D data acquisition, each network has limitations | 3D change detection [2] | |
| Advanced machine learning method | Random Forest and CANUPO classification | supervised | Mobile LiDAR point cloud | Handles complex topography, efficient, automatic object extraction | Sensitive to parameter selection, CANUPO classification errors affect results | 3D change detection coastal line [120] | RMSE = 0.16m |
| CNN | Transformer-based MTBIT network | supervised | Bi-temporal optical images | No need for LiDAR or DSM, high accuracy, efficient | Noise generation, underestimation of changes, sensitive to loss weight | 3D change detection [121] | F1-score = 62.15% |
| CNN | Siamese KPConv network | supervised | 3D point clouds | Direct use of point clouds, no rasterization, robust, transfer learning capability, flexible | Computational expense, sensitive to hyperparameters, risk of overfitting | Urban 3D change detection [122] | mIOU = 80% |
| Comparison between machine learning methods | Review of pixel-based (SVM) and point-based (M3C2, cloud-to-cloud) methods | supervised | LiDAR data | Noise reduction and robustness | Thresholding challenges, residual errors, data availability issues | Building change detection [123] | Varies depending on method |
| CNN | Self-supervised learning with deep clustering | un-supervised | ALS point clouds | No need for training data, computationally efficient, direct raw data usage | Occlusion and vegetation challenges | 3D change detection [124] | Mean Accuracy = 85.2% |
| AE | YOLOv7 + U-Net (AE structure) multiple building change detection | supervised | Point cloud from dense stereo matching | Fully automatic, handles unbalanced data, detects multiple changes | Complex model, requires augmentation, needs testing on unbalanced data | Building change detection [9] | OA = 94.81% |
| Various models | LiDAR simulation tool for benchmarking | supervised | LiDAR | Simulation framework generates labeled data automatically | Simple structure, limited for complex 3D changes, needs supervision, sensitive to acquisition angle | Urban change detection [125] | Varies |
| Machine learning, deep learning | Review of 3D change detection methods | supervised | Point clouds | Distance-based simple, ML integrates classification and detection, deep learning improves results and handles occlusion better | Distance-based methods weak for surface changes, sensitive to point density, ML depends on training data, deep learning is complex and has imbalance issues | Urban change detection [126] | Varies |
| CNN | Introduction of new 2D and 3D dataset | supervised | 2D change map, 3D elevation data | New dataset with 2D and 3D data, reduced data requirement, publicly available | Limited dataset (Spain only) | Urban change detection [127] | - |
| AE | W-Net for 2D and 3D building change detection | supervised | LiDAR point cloud, optical images | Handles multisource and multifeature data, good boundary reconstruction | High computational cost, complex model, dependent on ground truth accuracy | Building change detection [76] | OA = 99.56 |
| Machine learning, deep learning, distance based | Review + simulation tool | supervised | point cloud | Automatic labeling, diverse scales | Simplifies urban environment, mislabels artifacts | Urban change detection [128] | Varies |
| Co-segment | 3D co-segmentation using morphological building indices and DSM | supervised | High-resolution satellite stereo image | Simultaneous 2D segmentation and 3D detection, robust to acquisition angles, improved boundary detection | Dependent on DSM quality, occlusion errors, difficulty in small changes | Building change detection [129] | F-score = 89.07 |
| CNN | Review + WCNN3D model for 3D object detection | supervised | LiDAR point clouds | Good performance for small objects, reduced information loss | High computational cost | 3D change detection in urban environments [130] | AP3D = 77.6% |
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Gomroki, M.; Gomroki, A.; Gulden, R.H.; Benaragama, D.I.; Hasanlou, M.; Badreldin, N.; Kalantar, B.; Al-Najjar, H. 2D and 3D Urban Change Detection Methods Using Remote Sensing: A Review. Remote Sens. 2026, 18, 1606. https://doi.org/10.3390/rs18101606
Gomroki M, Gomroki A, Gulden RH, Benaragama DI, Hasanlou M, Badreldin N, Kalantar B, Al-Najjar H. 2D and 3D Urban Change Detection Methods Using Remote Sensing: A Review. Remote Sensing. 2026; 18(10):1606. https://doi.org/10.3390/rs18101606
Chicago/Turabian StyleGomroki, Masoomeh, Amirreza Gomroki, Robert H. Gulden, Dilshan I. Benaragama, Mahdi Hasanlou, Nasem Badreldin, Bahareh Kalantar, and Husam Al-Najjar. 2026. "2D and 3D Urban Change Detection Methods Using Remote Sensing: A Review" Remote Sensing 18, no. 10: 1606. https://doi.org/10.3390/rs18101606
APA StyleGomroki, M., Gomroki, A., Gulden, R. H., Benaragama, D. I., Hasanlou, M., Badreldin, N., Kalantar, B., & Al-Najjar, H. (2026). 2D and 3D Urban Change Detection Methods Using Remote Sensing: A Review. Remote Sensing, 18(10), 1606. https://doi.org/10.3390/rs18101606

