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ARTICLES

Changes in moorland and heathland bird abundance in southwest England in relation to environmental change

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Pages 543-553 | Received 01 Mar 2016, Accepted 22 Sep 2016, Published online: 19 Oct 2016

Figures & data

Figure 1. Location of study area (unenclosed heathland and moorland; shaded areas) within Exmoor National Park in southwest England.

Figure 1. Location of study area (unenclosed heathland and moorland; shaded areas) within Exmoor National Park in southwest England.

Table 1. Abundance of moorland and heathland birds on Exmoor, UK BBS trends (Harris et al. Citation2015), UK Birds of Conservation Concern (BoCC4, Eaton et al. Citation2015), European red list status (BirdLife International Citation2015) and wintering zone of each species (Hayhow et al. Citation2014). Shown are the maximum (max) count of individuals in 2008 and 2014 across survey area, percentage change in maximum count between 2008 and 2014 and percentage change between 1995 and 2013 from UK-wide BBS data (*significant change at P < 0.05). No BBS trend data were available for Merlin or Dartford Warbler; instead abundance estimates for these species were derived from UK-wide national surveys in 1993–94 (Rebecca & Bainbridge Citation1998) and 2008 (Ewing et al. Citation2011), and 1994 (Gibbons & Wotton Citation1996) and 2006 (Wotton et al. Citation2009), respectively. Max count figures for Meadow Pipit and Skylark in 2008 and 2014 are counts from early visits only to exclude juveniles, and max count figures for Northern Wheatear in 2008 and 2014 are counts from late visits only to exclude migrants.

Table 2. Environmental variables, variable definitions, recording categories, which visit the data were recorded on, number of 200-m cells in which a change in each variable was recorded, and median values (i.e. summary values of categorical variables) of the 21 environmental variables surveyed in the field in 2008 and 2014. The change 2008–14 column shows whether the change between years in the median value for each variable was significant, using Wilcoxon matched pairs tests. Key: blank = no significant year effect; ---/+++ = decrease or increase at P < 0.001; --/++ = P < 0.01; -/+ = P < 0.05.

Table 3. Summary of GLMs testing for associations between change in bird abundance and change in environmental variables between 2008 and 2014. Data are presented only for environmental variables which showed significant associations with at least one bird species. Key: blank = no significant association; ---/+++ = negative or positive relationship at P < 0.001; --/++ at P < 0.01; -/+ at P < 0.05. No significant associations between Common Cuckoo, Grey Wagtail or Northern Wheatear abundance change and change in environmental variables were found in 168, 134 and 27 200 m sections, respectively.

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