Abstract

Detailed and accurate information on the spatial variation of land cover and land use is a critical component of local ecology and environmental research. For these tasks, high spatial resolution images are required. Considering the trade-off between high spatial and high temporal resolution in remote sensing images, many learning-based models (e.g., Convolutional neural network, sparse coding, Bayesian network) have been established to improve the spatial resolution of coarse images in both the computer vision and remote sensing fields. However, data for training and testing in these learning-based methods are usually limited to a certain location and specific sensor, resulting in the limited ability to generalize the model across locations and sensors. Recently, generative adversarial nets (GANs), a new learning model from the deep learning field, show many advantages for capturing high-dimensional nonlinear features over large samples. In this study, we test whether the GAN method can improve the generalization ability across locations and sensors with some modification to accomplish the idea “training once, apply to everywhere and different sensors” for remote sensing images. This work is based on super-resolution generative adversarial nets (SRGANs), where we modify the loss function and the structure of the network of SRGANs and propose the improved SRGAN (ISRGAN), which makes model training more stable and enhances the generalization ability across locations and sensors. In the experiment, the training and testing data were collected from two sensors (Landsat 8 OLI and Chinese GF 1) from different locations (Guangdong and Xinjiang in China). For the cross-location test, the model was trained in Guangdong with the Chinese GF 1 (8 m) data to be tested with the GF 1 data in Xinjiang. For the cross-sensor test, the same model training in Guangdong with GF 1 was tested in Landsat 8 OLI images in Xinjiang. The proposed method was compared with the neighbor-embedding (NE) method, the sparse representation method (SCSR), and the SRGAN. The peak signal-to-noise ratio (PSNR) and structural similarity (SSIM) were chosen for the quantitive assessment. The results showed that the ISRGAN is superior to the NE (PSNR: 30.999, SSIM: 0.944) and SCSR (PSNR: 29.423, SSIM: 0.876) methods, and the SRGAN (PSNR: 31.378, SSIM: 0.952), with the PSNR = 35.816 and SSIM = 0.988 in the cross-location test. A similar result was seen in the cross-sensor test. The ISRGAN had the best result (PSNR: 38.092, SSIM: 0.988) compared to the NE (PSNR: 35.000, SSIM: 0.982) and SCSR (PSNR: 33.639, SSIM: 0.965) methods, and the SRGAN (PSNR: 32.820, SSIM: 0.949). Meanwhile, we also tested the accuracy improvement for land cover classification before and after super-resolution by the ISRGAN. The results show that the accuracy of land cover classification after super-resolution was significantly improved, in particular, the impervious surface class (the road and buildings with high-resolution texture) improved by 15%.

Highlights

  • Detailed and accurate information on the spatial variation of land cover and land use is a critical component of local ecology and environmental research

  • The proposed method is compared to the neighbor-embedding (NE), sparse representation (SCSR), and the original super-resolution generative adversarial nets (SRGANs) methods, and the results show that the improved SRGAN (ISRGAN) achieved the best performance;

  • Trehde ipcrteeddicsteudpseurp-reers-roelsuoltuiotinonimimaaggee ffoorr oouur rISIRSGRAGNANmomdeol d(be)l o(nb)a oGnF a1 GdaFta1setdiantaset in GuangdGonuagn,gcdoomngp,acroemdptaoretdhteoitnhpe uintpiumt iamgaeg(ea()a)aannddtthhee ggrroouunnddtrturtuht(hc)(. cF)i.guFriegsu(rde),s((ed),)a,n(de)(,f)aanrde 1(:f1) are 1:1 plots of the Digital Number (DN) value in the red, green and blue bands compared to the ground plots of ttrhuethD(icg),itwailthNsulompebseorf(1D.0N06)3v, a1.l0u0e32i,natnhde0r.9e9d5,5g, rreesepnecatinvdelyb.lue bands compared to the ground truth (c), with slopes of 1.0063, 1.0032, and 0.9955, respectively

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Summary

Introduction

Detailed and accurate information on the spatial variation of land cover and land use is a critical component of local ecology and environmental research For these tasks, high spatial resolution images are required to capture the temporal and spatial dynamics of the earth’s surface processes [1]. The basic assumption of the image super-resolution model is that missing details in a low spatial resolution image can be either reconstructed or learned from other high spatial resolution images if these images follow the same resampling process as was used to create the low spatial resolution image Based on this assumption, in the last decade, efforts have been made to focus on accurately predicting the point spread function (PSF), which represents the mixture process that forms the low-resolution pixels. There are mainly three groups of methods: 1) interpolation-based methods, 2) refactoring-based methods, and 3) learning-based methods (Table 1)

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