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<oai_dc:dc xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:title xmlns:dc="http://purl.org/dc/elements/1.1/">Biodiversity patterns under a shifting baseline: Sensitive fish species core areas (Aim 1) 2024</dc:title>
  <dc:type xmlns:dc="http://purl.org/dc/elements/1.1/">dataset</dc:type>
  <dc:identifier xmlns:dc="http://purl.org/dc/elements/1.1/">https://portal.medin.org.uk/portal/start.php?tpc=009_CEFAS07428f33-233f-431a-a0a4-3210fe245c2a</dc:identifier>
  <dc:description xmlns:dc="http://purl.org/dc/elements/1.1/">The dataset contains outputs from Aim 1 in Bluemel et al. 2024 - Biodiversity 
patterns under a shifting baseline: important areas for sensitive fish species 
and ecosystem functioning to assist marine spatial planning (see attached), 
Cefas Project Report for Defra, 40 pp. The dataset includes regional 
core-areas (persistent areas of high fish population density) and projected 
spatial changes in the distribution of sensitive fish species (currently and 
under future environmental change) for nine focal species, including the 
common skate complex (Dipturus spp.), spurdog (Squalus acanthias), tope 
(Galeorhinus galeus), spotted ray (Raja montagui), undulate ray (Raja 
undulata), starry ray (Amblyraja radiata), John Dory (Zeus faber), Atlantic 
wolffish (Anarhichas lupus) and Atlantic halibut (Hippoglossus hippoglossus).

Historic core areas / home ranges: vectors of historic core-areas (persistent 
areas of high fish population density) and home ranges of the nine focal 
species derived from standardised trawl data (survey catch-rates expressed in 
terms of biomass per area swept by the trawl, kg.km2) from long-term 
fishery-independent monitoring programmes (Lynam &amp; Ribeiro 2022a). Where 
available, core areas were defined for each decade (1985 &#x2013; 1994; 1995 &#x2013; 2004; 
2005 &#x2013; 2014) where 50% of the population&#x2019;s kernel density was concentrated. 
Similarly, the species range was defined as the areas containing 95% of the 
population&#x2019;s kernel density. NB, there are no historic core areas available 
for tope.

Species distributions: contains gridded rasters of the raw predicted habitat 
suitability projections from the Bayesian Additive Regression Trees (BART, 
Chipman et al., 2010) modeling algorithm for the nine fish species for the 
model training/current day period 2005 &#x2013; 2014 ('Training') and expected 
habitat suitability for a species given future environmental conditions in 
2050 (climate projection representative concentration pathway (RCP) 4.5 
(medium emissions, high mitigation)) ('RCP4.5_2050').

Current core areas: contains vectors of current core-areas of the nine focal 
species derived from the expected habitat, based on a novel thresholding 
approach tailored to the projections of each species distribution model (SDM) 
by outcomes from the spatial analysis of survey-derived biomass. 

Future core areas under rcp4.5 emissions scenario in 2050: contains vectors of 
future core-areas of the nine focal species derived from the expected habitat, 
based on a novel thresholding approach tailored to the projections of each SDM 
by outcomes from the spatial analysis of survey-derived biomass. NB, no future 
core area is predicted for starry ray under this emissions scenario.

The spatial reference for all data is WGS84/UTM zone 30N (EPSG:32630)</dc:description>
  <dc:date xmlns:dc="http://purl.org/dc/elements/1.1/">20250411 20240502</dc:date>
</oai_dc:dc>
