This version available http://nora.nerc.ac.uk/511342/ NERC has developed NORA to enable users to access research outputs wholly or partially funded by NERC. Copyright and other rights for material on this site are retained by the rights owners. Users should read the terms and conditions of use of this material at http://nora.nerc.ac.uk/policies.html#access This document is the author's final manuscript version of the journal article, incorporating any revisions agreed during the peer review process. Some differences between this and the publisher's version remain. You are advised to consult the publisher's version if you wish to cite from this article.The definitive version is available at http://www.maneyonline.com/ Contact CEH NORA team at noraceh@ceh.ac.ukThe NERC and CEH trademarks and logos ('the Trademarks') are registered trademarks of NERC in the UK and other countries, and may not be used without the prior written consent of the Trademark owner. et al., 1993; Thompson et al., 2003; Thompson et al., 2012). 40The birds nest in the heaths and feed on invertebrates within the Racomitrium carpets, 41 e.g. tipulid larvae (Smith et al., 2001). However, there is concern that heavy grazing by 42 sheep is causing these heaths to decline in extent and change in composition with loss of 43Racomitrium (Thompson et al., 1987; Ratcliffe & Thompson, 1988; Thompson et al., 44 2012). Nitrogen deposition can also damage Racomitrium (Baddeley et al., 1994; Jones 45 et al., 2002; Pearce et al., 2003), and moreover helps the spread of graminoids 46 (Armitage, 2010); these are usually introduced into the heaths by sheep. The increased 47 cover of graminoids may then attract more herbivore usage, so the interaction of grazing 48 with nitrogen deposition substantially increases the overall threat to Racomitrium (Van 49 2 der Wal et al., 2003Wal et al., , 2011 Armitage et al., 2012). Over much of the British range of 1 this community there is monitoring of Special Areas of Conservation and SPAs to assess 2 if conservation targets are being met for habitats and birds respectively (see Van der Wal 3 et al., 2011, Thompson et al., 2012. However, we lack detailed data on the nature of 4 changes in vegetation and their drivers (e.g. Ross et al., 2012). 5 6 In 1990 we began detailed studies on a montane heath around the summit of Glas 7Maol, part of the Caenlochan SPA designated for its dotterel population. This mountain 8 in the eastern Scottish Highlands had long been grazed by sheep and had a substantial 9 breeding population of dotterel (Galbraith et al., 1993). Our study was triggered by the 10 construction of a fenced skiing corridor along the edge of the summit plateau in 1986; 11 this 800 m long corridor clearly modified sheep usage on Glas Maol since it prevented 12sheep from moving directly between favoured grazings on the summit and in an adjacent 13 corrie. The fencing also gave the sheep some shelter, causing greater usage close-by. 14 Furthermore, the fencing was designed to intercept drifting snow, increasing t...