satellite remote sensing of phytoplankton biomarker pigments: a … · 2018. 12. 5. · total...

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Satellite remote sensing of phytoplankton biomarker pigments: a statistical learning approach Andy Stock & Ajit Subramaniam, Lamont-Doherty Earth Observatory, Columbia University, New York, USA Acknowledgments This work was supported in part by the Gulf of Mexico Research Initiative’s "Ecosystem Impacts of Oil and Gas Inputs to the Gulf" (ECOGIG) program. This is ECOGIG contribution #529. This work was also supported by NASA OBB grant NNX16AAJ08G. References Vidussi F et al. (2001). Phytoplankton pigment distribution in relation to upper thermocline circulation in the eastern Mediterranean Sea during winter. Journal of Geophysical Research: Oceans, 106(C9), 19939-19956.. Roberts DR et al. (2017). Crossvalidation strategies for data with temporal, spatial, hierarchical, or phylogenetic structure. Ecography, 40(8), 913-929. Background. Phytoplankton are the base of the marine food web and have a major climate-regulating function. However, these ecosystem services depend on phytoplankton community composition, which is sensitive to climate change. One of the most important challenges in satellite monitoring of the world's oceans is thus the development of algorithms that can distinguish dierent phytoplankton functional types (PFTs) from space. Researchers have proposed various algorithms for this purpose (Mouw et al., 2017). Types of existing algorithms include abundance-based (using only chlorophyll-a concentrations as predictor), spectral (using remote sensing reectances) and ecological (using environmental predictors like sea surface temperature in addition to spectral data). However, these algorithms have not been fully validated, and past comparisons between dierent algorithm types have been inconclusive . Methods. We obtained in-situ HPLC measurements of the concentrations of eight pigments serving as biomarkers for PFTs (Vidussi et al., 2001) from NASA SeaBASS. We matched these observations with MODIS-Aqua spectral and other satellite data, yielding a data set of 442 observations (Figs. 1, 2). We then compared the performance of dierent abundance-based algo- rithms (implemented as smoothing splines), spectral algorithms and ecological algorithms (implemented as random forests). Given sparse and spatially clustered in-situ observations, we tuned and tested the dierent algorithms by means of hierarchical spatial block cross-validation (Roberts et al., 2017), an approach for estimating the extrapolation error of statistical models when observations are not independent. We used the best models to generate global maps of relative pigment concentrations. Results. Compared to a null model always predicting the mean of the training blocks, the best models identied by our approach reduced the cross-validated mean squared error (MSE) by 74% for fucoxanthin, 59% for zeaxanthin, and 26% for 19'- butanoyloxyfucoxanthin. For these 3 pigments, ecological models worked best, and abundance-based models worst, but the dierences were small for zeaxanthin. For all other pigments, improvements over the null model were small. Summary and conclusions. 1. We identied good models predicting relative concentrations of fucoxanthin and zeaxanthin. 2. For the other biomarker pigments, all tested models performed only little better than the null model (if at all), suggesting that multi- spectral and environmental data like SST are insucient predictors of the associated phytoplankton communities. Fig. 1. In-situ HPLC samples. Colors indicate spatial blocks, areas of bubbles are proportional to spatial declustering weights. but.fuco hex.fuco allo fuco perid zea dv_chl_b tot_chl_b Improvement of MSE over null model (%) 0 20 40 60 80 100 Best abundancebased model Best spectral model Best ecological model Fig. 3. Reduction of cross-validated error (MSE) for dierent algorithm types and pigments in comparison to a null model. Fig. 4. Mean predicted relative concentrations (proportion of total pigment) of fucoxanthin and zeaxanthin for June 2017. Fig. 2. Overview of predictors, responses and models. Mouw CB et al. (2017). A consumer's guide to satellite remote sensing of multiple phytoplankton groups in the global ocean. Frontiers in Marine Science, 4, 41.

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Page 1: Satellite remote sensing of phytoplankton biomarker pigments: a … · 2018. 12. 5. · total pigment) of fucoxanthin and zeaxanthin for June 2017. Fig. 2. Overview of predictors,

Satellite remote sensing of phytoplankton biomarker pigments:a statistical learning approach Andy Stock & Ajit Subramaniam, Lamont-Doherty Earth Observatory, Columbia University, New York, USA

AcknowledgmentsThis work was supported in part by the Gulf of Mexico Research Initiative’s "EcosystemImpacts of Oil and Gas Inputs to the Gulf" (ECOGIG) program. This is ECOGIG contribution#529. This work was also supported by NASA OBB grant NNX16AAJ08G.

References

Vidussi F et al. (2001). Phytoplankton pigment distribution in relation to upperthermocline circulation in the eastern Mediterranean Sea during winter. Journal ofGeophysical Research: Oceans, 106(C9), 19939-19956..

Roberts DR et al. (2017). Cross‐validation strategies for data with temporal, spatial,hierarchical, or phylogenetic structure. Ecography, 40(8), 913-929.

Background. Phytoplankton are the base of the marine foodweb and have a major climate-regulating function. However,these ecosystem services depend on phytoplankton communitycomposition, which is sensitive to climate change. One of themost important challenges in satellite monitoring of the world'soceans is thus the development of algorithms that candistinguish different phytoplankton functional types (PFTs) from space. Researchers have proposed various algorithms for thispurpose (Mouw et al., 2017). Types of existing algorithms includeabundance-based (using only chlorophyll-a concentrations aspredictor), spectral (using remote sensing reflectances) andecological (using environmental predictors like sea surfacetemperature in addition to spectral data). However, thesealgorithms have not been fully validated, and past comparisonsbetween different algorithm types have been inconclusive .

Methods. We obtained in-situ HPLC measurements of theconcentrations of eight pigments serving as biomarkers for PFTs (Vidussi et al., 2001) from NASA SeaBASS. We matched theseobservations with MODIS-Aqua spectral and other satellite data,yielding a data set of 442 observations (Figs. 1, 2). We then compared the performance of different abundance-based algo-rithms (implemented as smoothing splines), spectral algorithmsand ecological algorithms (implemented as random forests).Given sparse and spatially clustered in-situ observations, wetuned and tested the different algorithms by means ofhierarchical spatial block cross-validation (Roberts et al., 2017),an approach for estimating the extrapolation error of statisticalmodels when observations are not independent. We used thebest models to generate global maps of relative pigmentconcentrations.

Results. Compared to a null model always predicting the meanof the training blocks, the best models identified by ourapproach reduced the cross-validated mean squared error (MSE)by 74% for fucoxanthin, 59% for zeaxanthin, and 26% for 19'-butanoyloxyfucoxanthin. For these 3 pigments, ecologicalmodels worked best, and abundance-based models worst, butthe differences were small for zeaxanthin. For all otherpigments, improvements over the null model were small.

Summary and conclusions.

1. We identified good models predicting relative concentrationsof fucoxanthin and zeaxanthin.

2. For the other biomarker pigments, all tested models performedonly little better than the null model (if at all), suggesting that multi-spectral and environmental data like SST are insufficient predictorsof the associated phytoplankton communities.

Fig. 1. In-situ HPLC samples. Colors indicate spatial blocks,areas of bubbles are proportional to spatial declustering weights.

but.fuco hex.fuco allo fuco perid zea dv_chl_b tot_chl_b

Impr

ovem

ento

fMSE

over

nullm

odel

(%)

020

4060

8010

0 Best abundance−based modelBest spectral modelBest ecological model

Fig. 3. Reduction of cross-validated error (MSE) for differentalgorithm types and pigments in comparison to a null model.

Fig. 4. Mean predicted relative concentrations (proportion oftotal pigment) of fucoxanthin and zeaxanthin for June 2017.

Fig. 2. Overview of predictors, responses and models.

Mouw CB et al. (2017). A consumer's guide to satellite remote sensing of multiplephytoplankton groups in the global ocean. Frontiers in Marine Science, 4, 41.