Improving low-quality satellite remote sensing reflectance at blue bands over coastal and inland waters

https://doi.org/10.1016/j.rse.2020.112029Get rights and content

Highlights

  • A spectral shape based algorithm is developed to estimate Rrs(41×) and Rrs(443).

  • The algorithm can greatly increase the satellite Rrs data quality and quantity.

  • It allows for more accurate and increased number of valid ocean color retrievals.

Abstract

The satellite remote sensing reflectance (Rrs(λ)) at two short blue bands (410 or 412 nm and 443 nm) are prone to large uncertainties in coastal and inland waters, prohibiting algorithms from generating reliable ocean color products associated with these bands. In this study, we developed an algorithm to estimate Rrs(41×) and Rrs(443) when the satellite Rrs(λ) in blue bands suffer from large uncertainties. The algorithm first determines the Rrs(λ) spectral shape from the satellite-measured Rrs(λ) values at three wavelengths of 48× (486, 488, or 490), 55× (547, 551, or 555), and 67× (667, 670, or 671) nm. The algorithm then derives Rrs(41×) and Rrs(443) from the estimated Rrs(λ) spectral shape with algebraic formulations. We assessed the algorithm performance with satellite (SeaWiFS, MODISA, and VIIRS-SNPP) and in situ Rrs(λ) matchups from global waters. It is shown that the uncertainties of estimated Rrs(41×) and Rrs(443) are substantially smaller than the original satellite products when applicable. Besides, implementation of the algorithm contributes to a significant increase in the number of utilizable Rrs(41×) and Rrs(443) values. The algorithm is relatively stable and is best applicable to the satellite Rrs(λ) spectra for which the Rrs(48×) and Rrs(55×) measurements are subject to small uncertainties. The demonstrations support the application of the blue-band estimation algorithm to a wide range of coastal waters.

Introduction

Ocean color satellites provide a means of collecting remote sensing reflectance (Rrs(λ)) on spatial and temporal scales unattainable by conventional in situ measurements. The Rrs(λ) data allow for the derivation of important biological and biogeochemical properties of the upper oceans, such as phytoplankton chlorophyll-a concentration (Chl) (Hu et al., 2012; McClain, 2009; Wang and Son, 2016), phytoplankton light absorption (Wang et al., 2017; Wei and Lee, 2015), colored dissolved organic matter (CDOM) absorption (Mannino et al., 2014; Wei et al., 2016a; Yu et al., 2016), and primary production (Behrenfeld et al., 2005; Lee et al., 2015a). For reliable estimation of these bio-optical properties, it is vital to obtain accurate Rrs(λ) product from satellites over a wide spectral domain, particularly at the blue bands of 41× (410 or 412) nm and 443 nm.

The ocean color satellites, including the decommissioned Sea-viewing Wide Field-of-view Sensor (SeaWiFS, 1997–2010) and the operational Moderate Resolution Imaging Spectroradiometer (MODIS) onboard the Aqua satellite (MODISA, 2002–present) and Visible Infrared Imaging Radiometer Suite (VIIRS) onboard the Suomi National Polar-orbiting Partnership satellite (VIIRS-SNPP, 2011–present), retrieve Rrs(λ) from the radiance measured at the top of atmosphere (TOA) through atmospheric correction (AC). Operational AC algorithms usually start with the selection of an aerosol model by assuming null contribution of water-leaving radiance (Lw(λ)) at the near-infrared (NIR) or shortwave infrared (SWIR) bands (Antoine and Morel, 1999; Gordon and Wang, 1994; Wang, 2007; Wang and Shi, 2007). This “black-pixel” assumption works well in open oceans, but is faced with some difficulties in coastal regions using the NIR and SWIR approach. The strongly absorbing aerosols, for instance, can be prominent in the coastal waters near anthropogenic sources of fossil-burning products, soot, and smog, or under the influence of dust transport. The weakly or strongly absorbing aerosols are hardly discriminable from radiance measurements in the NIR/SWIR domain but quite distinctive at short blue wavelengths (IOCCG, 2010). That being said, the standard AC schemes cannot correctly estimate the strongly absorbing aerosols and often fail to yield robust Rrs(λ) products at the blue wavelengths in many coastal regions due to lack of aerosol vertical distribution information (IOCCG, 2010; Kahn et al., 2016). As a consequence, and expectedly, the satellite-derived Rrs(41×) and Rrs(443) products are prone to large uncertainties in the coastal waters (Antoine et al., 2008; Feng et al., 2008; Hlaing et al., 2013; Qin et al., 2017; Zibordi et al., 2009). Apart from atmospheric correction, the large uncertainty in satellite Rrs(41×) product is also related to system vicarious calibration and instrument degradation (Franz et al., 2018). The relatively large uncertainties at blue bands and the subsequent lack of utilizable data at these two bands add to the difficulties of satellite ocean color applications in coastal regions (Mouw et al., 2015).

To address the blue-band Rrs(λ) quality issues, a great deal of effort has been invested. Gordon et al. (1997) and Chomko and Gordon (2001) developed an AC procedure to quantify the strongly absorbing aerosol contribution under dust-dominating conditions. Application of their methods, however, remains impractical because the vertical distribution of absorbing aerosols in the atmosphere is not known a priori (Banzon et al., 2009; IOCCG, 2010). In another case study, Hu et al. (2000) tested a nearest-neighbor method to account for the aerosol contribution at the NIR bands, with reasonable results. Variants of the standard AC schemes also emerged. Oo et al. (2008) reported improved atmospheric correction for turbid coastal waters by placing constraints onto Rrs(412) within their AC procedures. For highly absorptive waters, He et al. (2012) proposed null water-leaving radiance at 412 nm so as to make a guess of the aerosol contribution at that band, which was then used for atmospheric correction. In analogy, Wang and Jiang (2018) forced the negative Rrs(410) values from VIIRS-SNPP to zeroes to estimate the aerosol contributions and ultimately to obtain improved Rrs(λ) products.

Besides the above contributions, there exists another line of methodology to deal with the blue-band Rrs(λ) measurements. Basically, this category of methods attempts to “correct” the problematic blue-band Rrs(λ) data. In this regard, Ransibrahmanakul and Stumpf (2006) tested a power-law function to account for the spectral artifacts caused by the absorbing aerosols in the northeast U.S. coasts. D'Alimonte et al. (2008) derived multi-linear regression coefficients from satellite and in situ Rrs(λ) matchups and further applied those coefficients to estimate Rrs(412) for the same region. Undoubtedly, all strategies mentioned above have demonstrated varying degrees of success, specific to the sensors, dataset, or environments, in improving blue-band Rrs(λ) quality. Yet, it remains an open question to implement such algorithms as a universal approach to global coastal and inland waters where the satellite Rrs(41×) and Rrs(443) data are of low quality.

The blue-band Rrs(λ) data are needed for many bio-optical retrievals in the upper water columns. Among others, Rrs(41×) and Rrs(443) are indispensable for many semi-analytical algorithms to retrieve the phytoplankton and CDOM absorption coefficients from multiband satellite Rrs(λ) (IOCCG, 2006; Lee et al., 2002; Wei et al., 2019; Werdell et al., 2013). Rrs(443) data may also be required for Chl estimation in both open and coastal oceans (Hu et al., 2012; O'Reilly et al., 1998; Wang and Son, 2016). Use of Rrs(41×) and Rrs(443) data with large errors can result in unrealistic retrievals for the water bio-optical properties (Werdell et al., 2018) and biased Chl products (Hyde et al., 2007). It is also risky that merging of such satellite products may generate spurious trends in ocean color time series. In order to best interpret the large-scale and long-term ocean color retrievals, this long-standing problem associated with the blue-band satellite Rrs(λ) measurements needs to be resolved.

In this study, we propose a spectral shape based algorithm to estimate Rrs(41×) and Rrs(443) when the satellite Rrs(λ) spectra at blue bands are subjected to large uncertainties. Such estimation will help ultimately enhance the bio-optical retrievals with the ocean color algorithms requiring Rrs(41×) and/or Rrs(443) data. In the following, we first describe the evaluation data from SeaWiFS, MODISA, and VIIRS-SNPP, the proposed algorithm, and relevant analyses (Section 2). Next, we demonstrate the algorithm performance in estimating Rrs(41×) and Rrs(443) by comparison with in situ matchup measurements (Section 3). Finally, we discuss the algorithm applicability, uncertainty, potential impacts on satellite bio-optical retrievals, and potential applications to satellite image processing (Section 4).

Section snippets

Satellite and in situ Rrs(λ) matchups

The present study is based on satellite Rrs(λ) spectra and concurrent in situ matchup measurements. There were 2540 and 3639 matchups extracted for SeaWiFS and MODISA, respectively, from the SeaWiFS Bio-optical Archive and Storage (SeaBASS) (Werdell and Bailey, 2005). A total of 2348 matchups were also assembled for VIIRS-SNPP, with the in situ and satellite Rrs(λ) obtained from SeaBASS and NOAA CoastWatch, respectively. The Rrs(λ) matchups were constructed in accordance with the availability

Comparison of satellite and in situ Rrs(λ) matchups

We first assessed the satellite Rrs(48×), Rrs(55×), and Rrs(67×) uncertainties based on the satellite and in situ matchups as the Rrs(λ) data quality at these three bands is important for the implementation of the BBE algorithm. Comparisons of three groups of analyses in Table 2 indicate that the satellite Rrs(48×), Rrs(55×), and Rrs(67×) are prone to increasingly larger uncertainties with the decrease of QA scores, and vice versa. For the high-QA satellite data, specifically, Rrs(48×) and Rrs

Why the algorithm works

The BBE algorithm infers the Rrs(λ) spectral shapes through a spectral matching procedure using initial satellite Rrs(λ) values measured at 48×, 55×, and 67× nm and subsequently estimates Rrs(41×) and Rrs(443). It is based on an implicit assumption that the normalized satellite Rrs(λ) values at 41× and 443 nm are approximately equal to those selected from the LUT after the spectral matching. According to the validation results, this assumption is reliable for the estimation of Rrs(λ) at blue

Conclusions

Accurate retrieval of remote sensing reflectance in the two short blue bands of 41× nm and 443 nm in coastal and inland waters from ocean color satellites has been a challenge because of the complex oceanic and atmospheric properties. Whereas great effort has been put in, a considerable proportion of satellite reflectance products are still found susceptible to large uncertainties. In this study, we developed a spectral shape based algorithm to estimate Rrs(41×) and Rrs(443). The algorithm uses

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgments

We thank the NASA Ocean Biology Processing Group and SeaBASS for processing the satellite remote sensing reflectance data and archiving and distributing the in situ matchup data. The principal investigators, including those responsible for AERONET-OC observatories, are appreciated for sharing their field measurements. Thanks are also due to the NOAA Center for Satellite Applications and Research (STAR) and CoastWatch for processing and distributing the VIIRS-SNPP ocean color data. This study

References (68)

  • A. Morel et al.

    A simple band ratio technique to quantify the colored dissolved and detrital organic material from ocean color remotely sensed data

    Remote Sens. Environ.

    (2009)
  • C.B. Mouw et al.

    Aquatic color radiometry remote sensing of coastal and inland waters: challenges and recommendations for future satellite missions

    Remote Sens. Environ.

    (2015)
  • P. Qin et al.

    Radiometric validation of atmospheric correction for MERIS in the Baltic Sea based on continuous observations from ships and AERONET-OC

    Remote Sens. Environ.

    (2017)
  • M. Wang et al.

    VIIRS-derived chlorophyll-a using the ocean color index method

    Remote Sens. Environ.

    (2016)
  • M. Wang et al.

    Evaluation of MODIS SWIR and NIR-SWIR atmospheric correction algorithm using SeaBASS data

    Remote Sens. Environ.

    (2009)
  • J. Wei et al.

    An assessment of Landsat-8 atmospheric correction schemes and remote sensing reflectance products in coral reefs and coastal turbid waters

    Remote Sens. Environ.

    (2018)
  • P.J. Werdell et al.

    An improved bio-optical data set for ocean color algorithm development and satellite data product validation

    Remote Sens. Environ.

    (2005)
  • P.J. Werdell et al.

    An overview of approaches and challenges for retrieving marine inherent optical properties from ocean color remote sensing

    Prog. Oceanogr.

    (2018)
  • X. Yu et al.

    Light absorption properties of CDOM in the Changjiang (Yangtze) estuarine and coastal waters: an alternative approach for DOC estimation

    Estuar. Coast. Shelf Sci.

    (2016)
  • G. Zibordi et al.

    Validation of satellite ocean color primary products at optically complex coastal sites: Northern Adriatic Sea, Northern Baltic Proper and Gulf of Finland

    Remote Sens. Environ.

    (2009)
  • Z. Ahmad et al.

    New aerosol models for the retrieval of aerosol optical thickness and normalized water-leaving radiances from the SeaWiFS and MODIS sensors over coastal regions and open oceans

    Appl. Opt.

    (2010)
  • D. Antoine et al.

    A multiple scattering algorithm for atmospheric correction of remotely sensed ocean colour (MERIS instrument): principle and implementation for atmospheres carrying various aerosols including absorbing ones

    Int. J. Remote Sens.

    (1999)
  • D. Antoine et al.

    Assessment of uncertainty in the ocean reflectance determined by three satellite ocean color sensors (MERIS, SeaWiFS and MODIS-A) at an offshore site in the Mediterranean Sea (BOUSSOLE project)

    J. Geophys. Res.

    (2008)
  • S.W. Bailey et al.

    Estimation of near-infrared water-leaving reflectance for satellite ocean color data processing

    Opt. Express

    (2010)
  • M.J. Behrenfeld et al.

    Carbon-based ocean productivity and phytoplankton physiology from space

    Glob. Biogeochem. Cycles

    (2005)
  • A. Bricaud et al.

    Variability in the chlorophyll-specific absorption coefficients of natural phytoplankton: analysis and parameterization

    J. Geophys. Res.

    (1995)
  • A. Bricaud et al.

    Variations of light absorption by suspended particles with chlorophyll a concentration in oceanic (case 1) waters: analysis and implications for bio-optical models

    J. Geophys. Res.

    (1998)
  • A. Bricaud et al.

    Natural variability of phytoplanktonic absorption in oceanic waters: influence of the size structure of algal populations

    J. Geophys. Res.

    (2004)
  • K.L. Carder et al.

    Semianalytic Moderate-resolution Imaging Spectrometer algorithms for chlorophyll-a and absorption with bio-optical domains based on nitrate-depletion temperatures

    J. Geophys. Res.

    (1999)
  • R.M. Chomko et al.

    Atmospheric correction of ocean color imagery: test of the spectral optimization algorithm with the Sea-viewing Wide Field-of-View Sensor

    Appl. Opt.

    (2001)
  • D. D’Alimonte et al.

    A statistical method for generating cross-mission consistent normalized water-leaving radiances

    IEEE Trans. Geosci. Remote Sens.

    (2008)
  • H. Feng et al.

    Evaluation of MODIS Ocean colour products at a northeast United States coast site near the Martha’s Vineyard coastal observatory

    Int. J. Remote Sens.

    (2008)
  • Franz, B.A., Bailey, S.W., Eplee Jr, R.E., Lee, S., Patt, F.S., Proctor, C., & Meister, G. (2018). NASA multi-mission...
  • H.R. Gordon et al.

    Retrieval of water-leaving radiance and aerosol optical thickness over the oceans with SeaWiFS: a preliminary algorithm

    Appl. Opt.

    (1994)
  • Cited by (26)

    • Global satellite water classification data products over oceanic, coastal, and inland waters

      2022, Remote Sensing of Environment
      Citation Excerpt :

      We stress that the Class 16–23 waters are usually representative of turbid nearshore environments (recall Fig. 3). Accurate satellite retrieval of Rrs(λ) in such waters remains a challenge (Wang and Jiang, 2018; Wei et al., 2020; Zibordi et al., 2009a). Uncertainties in satellite Rrs(λ) data will be primarily responsible for the increased uncertainties in water class products (see further discussion in Section 5.3).

    View all citing articles on Scopus
    View full text