Abstract
Red tides caused by Margalefidinium polykrikoides occur continuously along the southern coast of Korea, where there are many aquaculture cages, and therefore, prompt monitoring of bloom water is required to prevent considerable damage. Satellite-based ocean-color sensors are widely used for detecting red tide blooms, but their low spatial resolution restricts coastal observations. Contrarily, terrestrial sensors with a high spatial resolution are good candidate sensors, despite the lack of spectral resolution and bands for red tide detection. In this study, we developed a U-Net deep learning model for detecting M. polykrikoides blooms along the southern coast of Korea from PlanetScope imagery with a high spatial resolution of 3 m. The U-Net model was trained with four different datasets that were constructed with randomly or non-randomly chosen patches consisting of different ratios of red tide and non-red tide pixels. The qualitative and quantitative assessments of the conventional red tide index (RTI) and four U-Net models suggest that the U-Net model, which was trained with a dataset of non-randomly chosen patches including non-red tide patches, outperformed RTI in terms of sensitivity, precision, and F-measure level, accounting for an increase of 19.84%, 44.84%, and 28.52%, respectively. The M. polykrikoides map derived from U-Net provides the most reasonable red tide patterns in all water areas. Combining high spatial resolution images and deep learning approaches represents a good solution for the monitoring of red tides over coastal regions.
Highlights
Margalefidinium polykrikoides blooms occur in Korean coastal waters in a repetitive manner
A U-Net deep learning model was developed for M. polykrikoides red tide detection on the southern coast of Korea from PlanetScope imagery with a high spatial resolution of 3 m
The major results are as follows: (1) We identified a distinct M. polykrikoides red tide pattern that distinguishes it from the surrounding waters using the PlanetScope image
Summary
Margalefidinium polykrikoides blooms occur in Korean coastal waters in a repetitive manner. This type of bloom has gradually become larger, wider, and more frequent since first appearing in 1995 [1,2]. M. polykrikoides blooms with a cell abundance greater than 1000 cells mL−1 can have a negative impact on fish or shellfish [3]. Large-scale M. polykrikoides blooms first formoffshore and are generally transported to coastal waters, where they gradually accumulate [4]. Because there are many aquaculture cages found along the south coast of Korea, The occurrence of blooms with a high cell abundance in this area would cause considerable economic damage. Since the outbreak of red tide blooms in
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