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. 2012 Jul 11;279(1743):3853–3860. doi: 10.1098/rspb.2012.0856

Figure 1.

Figure 1.

Proportional change in summed incidence of bird species between the two years (2003/2004 and 2007/2008) were compared using Mann–Whitney–Wilcoxon comparison of means (one-tailed), for the 12 mistletoe-free sites (grey), 11 control sites (black) and 17 treatment sites (white). (a) Summary of changes for those species that regularly forage on mistletoe nectar and/or fruit (31 species, of which 24 are woodland-dependent; after Reid [28]). No significant differences were detected, and prediction 2 was not supported. (b) Summary of changes for those species that have been recorded nesting in mistletoe clumps (67 species, of which 48 are woodland-dependent; after Cooney et al. [12]). Significant differences between means for treatment and control sites were detected (p = 0.008); treatment sites lost a greater proportion of mistletoe nesters than control sites, supporting prediction 3.