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clustering of abundance data from the OneBenthic database (see 
`https://sway.office.com/HM5VkWvBoZ86atYP?ref=Link`_). The second file, 
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modelled output, with darker shades (high values) indicating higher confidence 
and lighter shades (lower values) indicating lower confidence. Both layers can 
be viewed in the OneBenthic Layers tool *(
`https://rconnect.cefas.co.uk/onebenthic_layers/`_)*, together with further 
details of the methodology used to produce them.


.. _`https://sway.office.com/hm5vkwvboz86atyp?ref=link`:
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– Please note the applicable attribution statement is as follows: includes 
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modelling of point sample data from the OneBenthic *(OB, 
`https://rconnect.cefas.co.uk/onebenthic_dashboard`_/)* dataset, largely 
following the methodology in Cooper et al. (2019), but with an expanded 
dataset covering the Greater North Sea and including data from the EurOBI
(`https://www.eurobis.org/`_) data repository. Of the 44,407 samples within 
OB, we selected a subset of 31,845 for which data were considered comparable 
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sieve and not taken from a known impacted site). Colonial taxa were included 
and given a value of one. To take account of potential differences in 
taxonomic resolution between surveys, macrofaunal data were aggregated to 
family level using the taxonomic hierarchy provided by the World Register of 
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from the dataset, reducing the overall number to 18,348. A fourth-root 
transformation was then applied to the data to down weight the influence of 
highly abundant taxa. Data were then subjected to clustering using k-means. A 
species distribution modelling approach, based on random forest, was then used 
to model cluster group (i.e. macrofaunal assemblage or biotope) identity 
across the study area (Greater North Sea). Cross-validation via repeated 
sub-sampling was done to evaluate the robustness of the model estimate and 
predictions to data sub-setting and to extract additional information from the 
model outputs to produce maps of confidence in the predicted distribution, 
following the approach described in Mitchell et al. (2018). The 
cross-validation was done on 10 split sample data sets with 75% used to train 
and 25% to test models, randomly sampled within the levels of the response 
variable to maintain the class balance. The final model output was plotted as 
the cluster class with the majority vote of all 10 model runs. An associated 
confidence map was produced by multiplying map layers for 1) the frequency of 
the most common class and ii) the average probability of the most common 
class. Model outputs are used in the OneBenthic Layers Tool (
`https://rconnect.cefas.co.uk/onebenthic_layers/)`_.

Cooper, K.M.; Bolam, S.G.; Downie, A.-L.; Barry, J. 2019. Biological-based 
habitat classification approaches promote cost-efficient monitoring: An 
example using seabed assemblages. J. Appl. Ecol. 56:1085–1098. 
`https://doi.org/10.1111/1365-2664.13381`_

Mitchell, P.J., Downie, A.-L., Diesing, M. How good is my map? 2018. A tool 
for semi-automated thematic mapping and spatially explicit confidence 
assessment. Env. Model. Softw. 108, 111–122. 
`https://doi.org/10.1016/j.envsoft.2018.07.014`_


.. _`https://rconnect.cefas.co.uk/onebenthic_dashboard`:
    https://rconnect.cefas.co.uk/onebenthic_dashboard

.. _`https://www.eurobis.org/`:
    https://www.eurobis.org/

.. _`https://www.marinespecies.org/`:
    https://www.marinespecies.org/

.. _`https://rconnect.cefas.co.uk/onebenthic_layers/)`:
    https://rconnect.cefas.co.uk/onebenthic_layers/)

.. _`https://doi.org/10.1111/1365-2664.13381`:
    https://doi.org/10.1111/1365-2664.13381

.. _`https://doi.org/10.1016/j.envsoft.2018.07.014`:
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