Modelling the spatial distribution of cetaceans in New Zealand waters
|Author(s)||Stephenson Fabrice1, Goetz Kimberly2, Sharp Ben R.3, Mouton Theophile4, Beets Fenna L.1, Roberts Jim2, Macdiarmid Alison B.2, Constantine Rochelle5, 6, Lundquist Carolyn J.1, 6, Sarmento Cabral Juliano|
|Affiliation(s)||1 : National Institute of Water and Atmospheric Research (NIWA) Hamilton, New Zealand
2 : National Institute of Water and Atmospheric Research (NIWA) Wellington ,New Zealand
3 : Fisheries New Zealand Ministry for Primary Industries Wellington ,New Zealand
4 : Marine Biodiversity, Exploitation, and Conservation (MARBEC) UMR 9190 Université de Montpellier Montpellier, France
5 : School of Biological Sciences University of Auckland Auckland ,New Zealand
6 : Institute of Marine Science University of Auckland Auckland ,New Zealand
|Source||Diversity And Distributions (1366-9516) (Wiley), 2020-04 , Vol. 26 , N. 4 , P. 495-516|
|WOS© Times Cited||16|
|Keyword(s)||boosted regression tree models, cetacean distribution, New Zealand, relative environmental suitability models, spatial management, species distribution models|
Cetaceans are inherently difficult to study due to their elusive, pelagic and often highly migratory nature. New Zealand waters are home to 50% of the world's cetacean species, but their spatial distributions are poorly known. Here, we model distributions of 30 cetacean taxa using an extensive at‐sea sightings dataset (n > 14,000) and high‐resolution (1 km2) environmental data layers.
New Zealand's Exclusive Economic Zone (EEZ).
Two models were used to predict probability of species occurrence based on available sightings records. For taxa with <50 sightings (n = 15), Relative Environmental Suitability (RES), and for taxa with ≥50 sightings (n = 15), Boosted Regression Tree (BRT) models were used. Independently collected presence/absence data were used for further model evaluation for a subset of taxa.
RES models for rarely sighted species showed reasonable fits to available sightings and stranding data based on literature and expert knowledge on the species' autecology. BRT models showed high predictive power for commonly sighted species (AUC: 0.79–0.99). Important variables for predicting the occurrence of cetacean taxa were temperature residuals, bathymetry, distance to the 500 m isobath, mixed layer depth and water turbidity. Cetacean distribution patterns varied from highly localised, nearshore (e.g., Hector's dolphin), to more ubiquitous (e.g., common dolphin) to primarily offshore species (e.g., blue whale). Cetacean richness based on stacked species occurrence layers illustrated patterns of fewer inshore taxa with localised richness hotspots, and higher offshore richness especially in locales of the Macquarie Ridge, Bounty Trough and Chatham Rise.
Predicted spatial distributions fill a major knowledge gap towards informing future assessments and conservation planning for cetaceans in New Zealand's extensive EEZ. While sightings datasets were not spatially comprehensive for any taxa, these two best available approaches allow for predictive modelling of both more common, and of rarely sighted, cetacean species with limited available information.