Abstract

To be able to simulate spatial patterns of predator-prey interactions, many spatially-explicit ecosystem modeling platforms, including Atlantis, need to be provided with distribution maps defining the annual or seasonal spatial distributions of functional groups and life stages. We developed a methodology combining extrapolation and interpolation of the predictions made by statistical habitat models to produce distribution maps for the fish and invertebrates represented in the Atlantis model of the Gulf of Mexico (GOM) Large Marine Ecosystem (LME) (“Atlantis-GOM”). This methodology consists of: (1) compiling a large monitoring database, gathering all the fisheries-independent and fisheries-dependent data collected in the northern (U.S.) GOM since 2000; (2) compiling a large environmental database, storing all the environmental parameters known to influence the spatial distribution patterns of fish and invertebrates of the GOM; (3) fitting binomial generalized additive models (GAMs) to the large monitoring and environmental databases, and geostatistical binomial generalized linear mixed models (GLMMs) to the large monitoring database; and (4) employing GAM predictions to infer spatial distributions in the southern GOM, and GLMM predictions to infer spatial distributions in the U.S. GOM. Thus, our methodology allows for reasonable extrapolation in the southern GOM based on a large amount of monitoring and environmental data, and for interpolation in the U.S. GOM accurately reflecting the probability of encountering fish and invertebrates in that region. We used an iterative cross-validation procedure to validate GAMs. When a GAM did not pass the validation test, we employed a GAM for a related functional group/life stage to generate distribution maps for the southern GOM. In addition, no geostatistical GLMMs were fit for the functional groups and life stages whose depth, longitudinal and latitudinal ranges within the U.S. GOM are not entirely covered by the data from the large monitoring database; for those, only GAM predictions were employed to obtain distribution maps for Atlantis-GOM. Pearson residuals were computed to validate geostatistical binomial GLMMs. Ultimately, 53 annual maps and 64 seasonal maps (for 32 different functional groups/life stages) were produced for Atlantis-GOM. Our methodology could serve other world’s regions characterized by a large surface area, particularly LMEs bordered by several countries.

Highlights

  • Ecosystem simulation models are valuable tools for understanding the impacts of environmental and anthropogenic stressors on marine ecosystems and for informing resource management (Fulton, 2010; Christensen and Walters, 2011; O’Farrell et al, 2017)

  • Drexler and Ainsworth (2013) employed only one groundfish trawl survey dataset to produce all their distribution maps, which resulted in unreliable predictions of spatial distributions for those functional groups that are poorly sampled by groundfish trawl

  • Drexler and Ainsworth’s (2013) generalized additive models (GAMs) did not account for spatial autocorrelation, because their purpose was to be employed for performing extrapolation over the entire Gulf of Mexico (GOM) Large Marine Ecosystem (LME); this led to significant, unmodeled spatial patterns in Drexler and Ainsworth’s (2013) GAM residuals for functional groups associated with small-scale habitat features, such as red grouper (Epinephelus morio) and gag (Mycteroperca microlepis)

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Summary

Introduction

Ecosystem simulation models are valuable tools for understanding the impacts of environmental and anthropogenic stressors on marine ecosystems and for informing resource management (Fulton, 2010; Christensen and Walters, 2011; O’Farrell et al, 2017). To be able to represent patterns of spatial overlap between predators and prey, many spatially-explicit ecosystem modeling platforms, including Atlantis and OSMOSE, need to be provided with distribution maps defining the annual or seasonal spatial distributions of functional groups and life stages. The extrapolation of spatial distribution patterns predicted by statistical models integrating environmental covariates (commonly called “species distribution models”) is a useful means to produce distribution maps for spatially-explicit ecosystem models (Drexler and Ainsworth, 2013; Grüss et al, 2014, 2016d; Hattab et al, 2014). The authors extrapolated the predictions made by their GAMs to the entire GOM Large Marine Ecosystem (LME) to obtain distribution maps for some of the functional groups (all life stages combined) represented in the Atlantis model of the GOM LME (“Atlantis-GOM”; Figure 1). Drexler and Ainsworth’s (2013) GAMs did not account for spatial autocorrelation (spatial structure), because their purpose was to be employed for performing extrapolation over the entire GOM LME; this led to significant, unmodeled spatial patterns in Drexler and Ainsworth’s (2013) GAM residuals for functional groups associated with small-scale habitat features, such as red grouper (Epinephelus morio) and gag (Mycteroperca microlepis) (unpublished data)

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