Pescott, O.L.
ORCID: https://orcid.org/0000-0002-0685-8046; Powney, G.D.
ORCID: https://orcid.org/0000-0003-3313-7786; Roy, D.B.
ORCID: https://orcid.org/0000-0002-5147-0331.
2016
Approaches to Bayesian occupancy modelling for habitat quality assessment.
Wallingford, NERC/Centre for Ecology & Hydrology, 23pp.
Abstract
Bayesian ‘occupancy’ models (BOM) are a powerful tool that have recently been adapted to
deal with ‘opportunistic’ species data (i.e. biological records).
Individual species trends from any models can be aggregated to produce habitat indicators;
here this is demonstrated for BOMs and Frescalo (Hill, 2012) using two examples.
Example one demonstrates the production of habitat-specific trends using NPMS indicator
species and subsets of 1 x 1 km grid cells predicted to contain the habitat of interest from Land
Cover Mapping. Decisions around whether to include subsets of habitat-containing cells, or all
cells within a political boundary, will be important for trend interpretation: habitat subsets of
cells may lead to biases depending on true habitat change over time.
Example two compares BOMs to the Frescalo method, as well as investigating the impacts of
decisions for indicator production (e.g. weighting or not weighting by a species national
frequency) on the trends produced. In this example weighted trends for 18 Sphagnum species typical
of blanket bog were much more similar than unweighted trends.
In the case of contradictory habitat (or species) trends it will not normally be possible to
know which model is correct (at least in the absence of an unbiased dataset to which to refer).
Given that BOMs, as currently used, may contain significant bias, a prudent approach would be to
compare the outputs of several methods before making decisions.
Information
Programmes:
CEH Science Areas 2013- > Ecological Processes & Resilience
Library
Statistics
Downloads per month over past year
Metrics
Altmetric Badge
Dimensions Badge
Share
![]() |
