International Journal of Applied Earth Observation and Geoinformation
MODIS ocean color product downscaling via spatio-temporal fusion and regression: The case of chlorophyll-a in coastal waters
Introduction
Ocean color is an essential factor for understanding the dynamic ocean biosphere process (Esaias et al., 1998). Based on the high revisiting frequency (twice a day) of the Tarra and Aqua platforms, MODIS ocean color products from NASA have been widely used in the monitoring of ocean dynamics and global environment changes in the past few decades (Dasgupta et al., 2009; Esaias et al., 1998; McClain, 2009). Water quality in coastal waters, which reflects the interactions between humans and the local environment, is a common area of concern in ocean science (Cherukuru et al., 2016). However, the detailed information in coastal waters is difficult to capture using the NASA MODIS ocean-color products, considering the low spatial resolution of this data (1 km). Therefore, obtaining both high spatial and temporal resolution data in these areas is an urgent requirement for understanding the biological processes in coastal environments (Esaias et al., 1998; McClain, 2009).
In the last decade, efforts have been made to focus on how to improve the spatial resolution of coarse image observations in both computer vision and remote-sensing fields (Yang et al., 2010; Yue et al., 2016). Two major groups of techniques were developed to answer this question: image super-resolution techniques and spatiotemporal data fusion.
In the super-resolution field, the basic assumption is that the 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 (Fernandez-Beltran et al., 2016; Zurita-Milla et al., 2008). In these methods, the key step is to accurately predict the point spread function (PSF), which represents the mixture process that forms the low-resolution pixels (Yue et al., 2016). The PSF can be created based on image reconstruction (RE) technology, such as iterative back projection (IBP) and PSF deconvolution. These techniques extract certain physical properties and features to provide more detailed information about low spatial-resolution images and aggregate this information with regular interpolated results to obtain the final super-resolved image (Fisher and Mustard, 2004; Miskin and MacKay, 2000; Takeda et al., 2007). The point spread function can also be created based on image learning technologies when a large number of image samples are available, such as in convolutional neural network(CNN)(Dong et al., 2016), sparse coding (Yang et al., 2010), Bayesian networks (Lu and Qin, 2014), kernel-based methods (Takeda et al., 2007), and SVM-based methods (H. Zhang and Huang, 2013). However, in practice, the actual mixing process of low-resolution remote-sensing images could be too complex to be captured by one universal PSF based on limited samples. Furthermore, the accuracy of these methods decreases rapidly when the scale ratio gets larger. The common downscaling ratio of most super-resolution algorithms is 2–4. Conversely, the scale ratio between MODIS and Landsat data is 1 km/30 m = 33.3. With this huge difference of scales, these methods have limited application in downscaling MODIS data from 1 km to 30 m.
To avoid building the PSF and predicting image details, spatiotemporal data fusion techniques get higher spatial resolution texture details by merging fine images to coarse images, following certain rules. When there is no fine spatial resolution data available, fine time-series data is used as ancillary data to provide the details at the same location (Chen et al., 2015). These spatiotemporal data fusion techniques are based on two assumptions: the scale invariance of temporal information and the temporal constancy of spatial information (Zhang et al., 2015). Compared to super-resolution methods, time-series image fusion technology does not predict high-resolution details directly from the coarse data. Instead, it combines the details revealed in time-series high spatial-resolution images at the same location. Many applications have been established based on these techniques, such as crop progress at field scales (Gao et al., 2017), NDVI time series (Zhang et al., 2016), spatial and temporal surface reflectance dynamics (Emelyanova et al., 2013), gross primary productivity (Singh, 2011), vegetation seasonal dynamics (Zurita-Milla et al., 2009), forest disturbance (Hilker et al., 2009), and seasonal wetlands monitoring (Mizuochi et al., 2017). To the best of our knowledge, these spatiotemporal data fusion techniques haven’t been tested on ocean color products for data downscaling.
The Unmixing-based Spatial-Temporal Reflectance Fusion Model (U-STFM) introduced by Huang and Zhang was used as the spatiotemporal data fusion technique in this study because it was announced to be more adaptable to land-cover changes (Huang and Zhang, 2014). The U-STFM combines the change ratio in time series with the linear decomposition model of mixed pixels to provide a new processing structure for time-series image fusion on rapidly changing landscapes. This method has been well tested in land-cover change applications, such as MODIS land surface reflectance downscaling, and has demonstrated its effectiveness (Huang and Zhang, 2014). The question is how to use this model to face the downscaling problem in ocean color products.
When applying U-STFM to downscale the MODIS ocean color chlorophyll-a concentration products, two issues need to be addressed. Firstly, the U-STFM model requires the consistency of the change ratio in both fine and coarse time-series data. However, this consistency of the change ratio is destroyed by involving different models with bias and variance during atmosphere correction and chlorophyll-a retrieval processing in MODIS and Landsat ocean surface chlorophyll-a concentration products (e.g., instrument calibration, atmospheric correction, inversion algorithms) (Pahlevan et al., 2016). Secondly, in U-STFM, it is necessary to decrease the size of the segmentation regions to obtain a more accurate changing ratio for each segmentation region in order to provide more detailed information in the final output. However, smaller regions may cause inconsistent solutions in the linear un-mixing equations, which will lead to data gaps or unreasonable predictions in the final output. More inconsistent solutions appear as “the hard boundaries” when applying U-STFM to detect more fragmented changes, such as the changes of chlorophyll-a concentration in coastal waters.
Therefore, in this study, we focus on these two main issues to extend the applications of U-STFM from inland areas to coastal waters for downscaling the spatial resolution of MODIS daily ocean surface chlorophyll-a concentration products from 1 km to 30 m. The Port of Tangshan Caofeidian in China, located in northeast Bohai Bay, was used as the case study area. Landsat 8 ground-truth remote-sensing reflectance (Rrs) and chlorophyll-a concentration products were used as reference data to assess the quality of final downscaled chlorophyll-a concentration products. In this study, the Rrs prediction results from the commonly used Spatial and Temporal Adaptive Reflectance Fusion Model (STARFM) (Gao et al., 2006) and Enhanced STARFM (ESTARFM) (Zhu et al., 2010) were also compared to the result from the U-STFM model. The major contributions of this study are as follows:
- •
Provides a way to extend the application of the U-STFM model from inland surface reflectance data to ocean color products.
- •
Predicts higher spatial resolution daily ocean surface chlorophyll-a concentration product in coastal water. The accuracy of this product remains the same as the original MODIS chlorophyll-a products but with more details in coastal waters.
- •
The method provided in this study can be further applied to other ocean color products, such as sea surface temperature, Kd490. This data can be further applied to build physical simulation models to better understand the dynamic changes in coastal waters.
Section snippets
Basic idea
The U-STFM model requires the same change ratio for pixels or regions on both fine and coarse spatial resolution time-series data. Since the consistency of the change ratio in MODIS and Landsat chlorophyll-a products can be destroyed by the different chlorophyll-a retrieval models (Pahlevan et al., 2016), it is difficult, if not impossible, to directly apply U-STFM on MODIS and Landsat chlorophyll-a products. However, compared to the processed products, the consistency of the change ratio can
Study area
Bohai Bay is one of the three bays forming the Bohai Gulf, the second largest gulf of the Bohai Sea in northeast China. Haihe and 15 other rivers drain into Bohai Bay. For this reason, the runoff of the whole eastern North China Plain is concentrated into Bohai Bay, and the bay is an intensely polluted body of water (Chen et al., 2010). Bohai Bay is ringed by several major ports: Tianjin port, Tangshan Caofeidian port, Jingtang port and Huanghua port, making the bay a crowded waterway. The
Predicting 30 m remote-sensing reflectance data using the U-STFM model
Twelve valid pairs of MODIS and Landsat 8 data were collected in this study. In this section, the targeted prediction date is set to Mar 10th, 2016. The results on other dates are also shown later. Because the U-STFM model requires three pairs (before-targeted-after date) for prediction, there are 24 before-targeted-after cases, leading to 24 predictions in total for the remote-sensing reflectance on Mar 10th, 2016. As is shown in Figure, the cloud cover and bad water pixels are masked as
Conclusions
Chlorophyll concentration rapidly change near coastal waters. In this study, we presented a method for downscaling the MODIS 1 km chlorophyll-a products to 30 m to better understand spatial variation of chlorophyll-a in coastal areas. To achieve this goal, two different correlations were used. Firstly, the correlation between different observations of time series at the same location were used to provide a detailed image texture to help us predict 30 m remote-sensing reflectance near the blue
Acknowledgements
This work was supported by the National Natural Science Foundation of China (Project No.: 41601212), the Fundamental Research Foundation of Shenzhen Technology and Innovation Council (Project No.: JCYJ20160429191127529), and the Fundamental Research Foundation of Shenzhen Technology and Innovation Council (Project No.: JSGG20150512145714247).
References (43)
- et al.
Estimating dissolved organic carbon concentration in turbid coastal waters using optical remote sensing observations
Int. J. Appl. Earth Observ. Geoinf.
(2016) - et al.
Retrieval of color producing agents in case 2 waters using Landsat 8
Remote Sens. Environ.
(2016) - et al.
Comparison of global chlorophyll concentrations using MODIS data
Adv. Space Res.
(2009) - et al.
Assessing the accuracy of blending Landsat-MODIS surface reflectances in two landscapes with contrasting spatial and temporal dynamics: a framework for algorithm selection
Remote Sens. Environ.
(2013) - et al.
High spatial resolution sea surface climatology from Landsat thermal infrared data
Remote Sens. Environ.
(2004) - et al.
Heavy metal pollution status in surface sediments of the coastal Bohai Bay
Water Res.
(2012) - et al.
Toward mapping crop progress at field scales through fusion of Landsat and MODIS imagery
Remote Sens. Environ.
(2017) - et al.
A new data fusion model for high spatial- and temporal-resolution mapping of forest disturbance based on Landsat and MODIS
Remote Sens. Environ.
(2009) - et al.
Development and evaluation of a lookup-table-based approach to data fusion for seasonal wetlands monitoring: an integrated use of AMSR series, MODIS, and Landsat
Remote Sens. Environ.
(2017) - et al.
Uncertainties in coastal ocean color products: impacts of spatial sampling
Remote Sens. Environ.
(2016)
Landsat 8 remote sensing reflectance (Rrs) products: evaluations, intercomparisons, and enhancements
Remote Sens. Environ.
Generation and evaluation of gross primary productivity using landsat data through blending with MODIS data
Int. J. Appl. Earth Observ. Geoinf.
Downscaling MODIS images with area-to-point regression kriging
Remote Sens. Environ.
An improved in-situ bio-optical data set for ocean color algorithm development and satellite data product validation
Remote Sens. Environ.
Image super-resolution : the techniques, applications, and future
Signal Process.
Application of synthetic NDVI time series blended from landsat and MODIS data for grassland biomass estimation
Remote Sens.
An enhanced spatial and temporal adaptive reflectance fusion model for complex heterogeneous regions
Remote Sens. Environ.
Downscaling time series of MERIS full resolution data to monitor vegetation seasonal dynamics
Remote Sens. Environ.
Coupling remote sensing retrieval with numerical simulation for SPM study-taking Bohai Sea in China as a case
Int. J. Appl. Earth Observ. Geoinf.
Comparison of spatiotemporal fusion models: a review
Remote Sens.
Image super-resolution using deep convolutional networks
IEEE Trans. Pattern Anal. Mach. Intell.
Cited by (16)
Progress of research on satellite remote sensing application in oceanography: A case study in China
2023, Regional Studies in Marine ScienceEstimating Ulva prolifera green tides of the Yellow Sea through ConvLSTM data fusion
2023, Environmental PollutionSpatiotemporal assessments of nutrients and water quality in coastal areas using remote sensing and a spatiotemporal deep learning model
2022, International Journal of Applied Earth Observation and GeoinformationCitation Excerpt :A low-cost and effective method for dynamic monitoring of widely distributed nutrients is urgently desired for spatially accurate management and environmental planning in coastal areas. Remote sensing techniques, which have the advantages of a larger spatial coverage and higher temporal frequency, have been applied to derive continually updated aquatic environmental information and have successfully produced detailed and consistent datasets for water quality analysis (Guo et al., 2018; He et al., 2020; Tran et al., 2019; Yacobi et al., 2011). However, remote sensing techniques are mainly applied to estimate aquatic environmental variables that contain optically active constituents, such as colored dissolved organic matter (CDOM), chlorophyll-a, and suspended particulate.
Combining Landsat-8 and Sentinel-2 to investigate seasonal changes of suspended particulate matter off the abandoned distributary mouths of Yellow River Delta
2021, Marine GeologyCitation Excerpt :However, sun-synchronous satellites (e.g., Landsat-5/7/8, Sentinel-2 and GF-1/2) can only capture instantaneous SPM distributions at the time of satellite overpass, and cannot continuously monitor the diurnal or hourly variations of SPM, such as during strong winds or a tidal cycle. Spatiotemporal data fusion techniques, developed by the remote sensing community in recent years, may be a feasible method to generate synthetic SPM images with both high spatial and high temporal resolution by fusing high temporal/low spatial resolution remote sensing images (e.g., MODIS, OLCI, and GOCI) and high spatial/low temporal resolution images (Guo et al., 2018; Liu et al., 2019; Pan et al., 2018). The satellite data related to this article included Landsat-8 OLI and Sentinel-2A/B MSI images which can be download from the U.S. Geological Survey's remote-sensing image database (https://earthexplorer.usgs.gov/) and the European Space Agency (https://sentinel.esa.int/web/sentinel/), respectively.