oceandatr
aims to provide simple functions for retrieving ocean data.
Using the associated package spatialgridr
, it can also easily grid
data, which is useful for various purposes including spatial
conservation prioritization.
Fish images in logo modified from original by Tracey Saxby, Integration and Application Network
You can install oceandatr from GitHub with:
if (!require(remotes)) install.packages("remotes")
#might need to increase timeout as it is a large package
options(timeout = 9999)
remotes::install_github("emlab-ucsb/oceandatr")
#load oceandatr package
library(oceandatr)
First we need a boundary for the area we are interested in. We can use
the get_boundary()
function, imported from spatialgridr
, to get a
boundary for land or ocean. In this example we will get Bermuda’s
Exclusive Economic Zone (EEZ)
bermuda_eez <- get_boundary(name = "Bermuda")
#plot to check we have Bermuda's EEZ
plot(bermuda_eez[1], col = "lightblue", main=NULL, axes=TRUE)
We are going to get gridded data. To create a grid for Bermuda, we use
get_grid()
. We need to provide a suitable projection for the area we
are interested in, https://projectionwizard.org is useful for this
purpose. Standard projections used for countries can also be found at
https://epsg.io/ by searching with country name. For spatial planning,
equal area projections are normally best.
The bounding box coordinates for the area of interest can be found using
sf::st_bbox(bermuda_eez)
and these can then be used to generate the
coordinate reference system (CRS) on projection
wizard
The coordinates above should be entered as the ‘Geographic extent’ and the map should then have a box drawn around the bounding box of the area of interest. The projection can then be copied and pasted from the pop-up box when clicking on ‘WKT’ or ‘PROJ’. For brevity, we are using the PROJ string, but WKT is now generally preferred. The projection needs to be placed in quotation marks as follows:
projection_bermuda <- '+proj=laea +lon_0=-64.8108333 +lat_0=32.3571917 +datum=WGS84 +units=m +no_defs'
We can now create a grid for Bermuda’s EEZ using get_grid()
. Along
with the projection we found above, we will need to set a resolution:
how wide and high will each grid cell be, in this case in metres. The
units will depend on your crs and can be found using
e.g. sf::st_crs(projection_bermuda, parameters = TRUE)$units_gdal
bermuda_grid <- get_grid(boundary = bermuda_eez, resolution = 5000, crs = projection_bermuda)
#project the eez into same projection as grid for plotting
bermuda_eez_projected <- bermuda_eez %>%
sf::st_transform(crs = projection_bermuda) %>%
sf::st_geometry()
#plot the grid
terra::plot(bermuda_grid, col = "gold3", axes = FALSE, legend = FALSE)
plot(bermuda_eez_projected, add=TRUE)
The raster covers Bermuda’s EEZ. The grid cells would be too small to see if we plotted them, but here is a coarser grid (lower resolution) visualized so we can see what the grid cells look like.
bermuda_grid_coarse <- get_grid(boundary = bermuda_eez, resolution = 20000, crs = projection_bermuda)
plot(bermuda_eez_projected, axes = FALSE)
terra::plot(terra::as.polygons(bermuda_grid_coarse, dissolve = FALSE), add=TRUE)
Now we have a grid, we can get some data. A key piece of data is
bathymetry. If the user has bathymetry data for their area of interest
already, they can pass the file path to this function and it will grid
the data using the supplied spatial grid. If no file path is provided,
the function will extract bathymetry data for the area from the ETOPO
2022 Global Relief
model
using a function borrowed from the
marmap
package.
bathymetry <- get_bathymetry(spatial_grid = bermuda_grid, classify_bathymetry = FALSE)
#> This may take seconds to minutes, depending on grid size
terra::plot(bathymetry, col = hcl.colors(n=255, "Blues"), axes = FALSE)
plot(bermuda_eez_projected, add=TRUE)
The ocean can be classified into 5 depth zones:
We can get the depth zones for Bermuda simply by setting the
classify_bathymetry
argument in get_bathymetry
to TRUE
.
depth_zones <- get_bathymetry(spatial_grid = bermuda_grid, classify_bathymetry = TRUE)
#> This may take seconds to minutes, depending on grid size
#value of 1 indicates that depth zone is present
terra::plot(depth_zones, col = c("grey60", "navyblue"), axes = FALSE, fun = function(){terra::lines(terra::vect(bermuda_eez_projected))})
The seafloor has its own valleys, plains and other geomorphological
features just as on land. These data come from Harris et al. 2014,
Geomorphology of the
Oceans and are available
for download from https://www.bluehabitats.org, but all but depth
classifications (which can be created using get_bathymetry()
) and
seamounts (which can be retrieved from a more recent dataset using
get_seamounts()
) are included in this package.
geomorphology <- get_geomorphology(spatial_grid = bermuda_grid) %>%
remove_empty_layers() #can remove any empty layers so we don't have so many layers to plot
#brown colour indicates that geomorphological feature is present
terra::plot(geomorphology, col = data.frame(c(0,1), c("grey60", "sienna")), axes = FALSE, legend = FALSE, fun = function(){terra::lines(terra::vect(bermuda_eez_projected))})
Knolls are another geomorphological feature, which are ‘small’ seamounts, classified as seamounts between 200 and 1000m higher than the surrounding seafloor Morato et al. 2008. Data are the knoll base area data from Yesson et al. 2011.
knolls <- get_knolls(spatial_grid = bermuda_grid)
#value of 1 indicates that knolls are present
terra::plot(knolls, col = c("grey60", "grey20"), axes = FALSE)
plot(bermuda_eez_projected, add=TRUE)
Seamounts, classified as peaks at least 1000m higher than the
surrounding seafloor Morato et
al. 2008. These data are from
Yesson et al. 2021.
Each peak is buffered to the distance specified in the function call.
The units of the buffer are in the same units as the spatial grid, which
can be checked using,
e.g. sf::st_crs(bermuda_grid, parameters = TRUE)$units_gdal
#spatial grid units are metres, so set buffer to 30000 m = 30 km
seamounts <- get_seamounts(spatial_grid = bermuda_grid, buffer = 30000)
#value of 1 indicates that seamount is present
terra::plot(seamounts, col = c( "grey60", "saddlebrown"), axes = FALSE)
plot(bermuda_eez_projected, add=TRUE)
Retrieve habitat suitability data for 3 deep water coral groups:
coral_habitat <- get_coral_habitat(spatial_grid = bermuda_grid)
#show the seamounts areas on the plot: coral habitat is often on seamounts which are shallower than surrounding ocean floor
#value of 1 indicates that coral is present
terra::plot(coral_habitat, col = c("grey60", "coral"), axes = FALSE, fun = function()terra::lines(terra::as.polygons(seamounts, dissolve = TRUE), col = "orangered4"))
Bioregions are often included in spatial planning, but available
bioregional classifications are either too coarse or too detailed to be
useful for planning at the EEZ level. Borrowing methods from Magris et
al. 2020, we use spatial clustering
of biophysical environmental data from
Bio-Oracle, to create ‘environmental
regions’. Biophysical conditions within a environmental region are more
similar than areas outside that region, though the differences may be
small. Diagnostic boxplots and a PCA will be shown if
show_plots = TRUE
. All the biophysical data are ocean surface data for
the period 2010 - 2020:
#set number of clusters to 3 to reduce runtime and memory usage
enviro_regions <- get_enviro_regions(spatial_grid = bermuda_grid, show_plots = TRUE, num_clusters = 3)
#value of 1 indicates that environmental region is present
terra::plot(enviro_regions, col = c("grey60", "forestgreen"), axes = FALSE, fun = function(){terra::lines(terra::vect(bermuda_eez_projected))})