Skip to main content
. 2022 Mar 2;9(3):211596. doi: 10.1098/rsos.211596

Table 1.

Environmental characteristics of 12 flightless, alpine New Zealand grasshopper species modelled in this study. The most important predictor of species distribution (from nine variables) is shown for each species (EMwms). Predictor variable importance scores for all models and all species are in electronic supplementary material, S8. Range-change percentages are based on the loss/gain/stability of pixels between vector binary maps (electronic supplementary material, S9). Predicted range changes include all gained pixels (with dispersal), while range change with no dispersal includes only gain of currently occupied habitat fragments.

species elevation range (m.a.s.l) number of presence points number of absence points most important predictor variable % range change from present (with dispersal)
% range change from present (no dispersal)
RCP2.6 RCP8.5 RCP2.6 RCP8.5
A. crassicauda 975–1680 16 933 mean diurnal range −43 208 −61 −11
A. tumidicauda 600–1830 49 900 precipitation of driest month −74 −35 −74 −37
B. collinus 1000–2000 30 919 mean diurnal range −95 −66 −96 −89
B. nivalis 450–2000 93 856 isothermality 59 134 −9 −7
P. dugdali 400–1160 29 920 precipitation seasonality −75 −96 −82 −97
P. nitidus 600–1830 91 858 mean temp. of driest quarter 12 17 −61 −35
S. australis 285–2020 278 671 annual mean temp. −74 −93 −75 −93
S. campestris 0–1550 100 849 soil −45 −67 −45 −67
S. childi 160–420 41 908 precipitation of driest month −47 154 −100 −89
S. minutus 500–1180 40 909 mean diurnal range 4 191 −80 −44
S. piliferus 725–1100 45 901 mean temp. of wettest quarter −15 −58 −45 −77
S. villosus 1370–2130 23 926 annual mean temp. 168 −77 −20 −94