Abstract

This study presents a novel method to identify optically deep water using purely spectral approaches. Optically deep waters, where the seabed is too deep for a bottom reflectance signal to be returned, is uninformative for seabed mapping. Furthermore, owing to the attenuation of light in the water column, submerged vegetation at deeper depths is easily confused with optically deep waters, thereby inducing misclassifications that reduce the accuracy of these seabed maps. While bathymetry data could mask out deeper areas, they are not always available or of sufficient spatial resolution for use. Without bathymetry data and based on the coastal aerosol blue green (1-2-3) bands of the Sentinel-2 imagery, this study investigates the use of band ratios and a false colour HSV transformation of both L1C and L2A images to separate optically deep and shallow waters across varying water quality over four tropical and temperate submerged sites: Tanzania, the Bahamas, the Caspian Sea (Kazakhstan) and the Wadden Sea (Denmark and Germany). Two supervised thresholds based on annotated reference data and an unsupervised Otsu threshold were applied. The band ratio group usually featured the best overall accuracies (OA), F1 scores and Matthews correlation coefficients, although the individual band combination might not perform consistently across different sites. Meanwhile, the saturation and hue band yielded close to best performance for the L1C and L2A images, featuring OA of up to 0.93 and 0.98, respectively, and a more consistent behaviour than the individual band ratios. Nonetheless, all these spectral methods are still susceptible to sunglint, the Sentinel-2 parallax effect, turbidity and water colour. Both supervised approaches performed similarly and were superior to the unsupervised Otsu’s method—the supervised methods featuring OA were usually over 0.70, while the unsupervised OA were usually under 0.80. In the absence of bathymetry data, this method could effectively remove optically deep water pixels in Sentinel-2 imagery and reduce the issue of dark pixel misclassification, thereby improving the benthic mapping of optically shallow waters and their seascapes.

Highlights

  • Since this study showed that different band pairs perform best at different sites, it would logically follow that a systematic optimisation approach such as Optimised Band Ratio Analysis (OBRA), Multiple Optimal Depth Predictors Analysis (MODPA) or SMART-satellite derived bathymetry (SDB) would provide competitive performances

  • This study showed the viability of a 1-2-3 false colour-derived saturation and hue band to separate the optically deep and shallow waters in Sentinel-2 L1C and

  • While some of the band ratios might have a slightly better performance quantitatively than the HSV bands, their individual performances are highly reliant on the water quality and, by extension, location

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Summary

Introduction

Coastal seascape ecosystems such as seagrasses and coral reefs provide a multitude of highly valued services such as coastal protection, biodiversity maintenance, blue carbon sequestration as well as nursery and feeding grounds for many marine animals [1]. These ecosystems are highly threatened and require urgent conservation and monitoring efforts [1,2]. Coastal aquatic remote sensing can help monitor these ecosystems by providing information on their benthic composition, water quality and bathymetry.

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