Summary of studies addressing the effects of disturbance on functional dispersion metrics across spatial scales
Ecosystem type . | Disturbance type . | Functional metric . | Increased spatial scale . | Effect of disturbance scale (ha) . | Reference . | ||
---|---|---|---|---|---|---|---|
. | . | . | . | Small/fine . | Intermediate . | Large . | . |
Arid shrubland | Rodent burrowing | FDisSES | ↓ | ↑ (10–4) | ↕ (0.01) | ↓ (0.25) | Current study |
Grasslands | Developing habitat (e.g. road verges and old fields) | MPDSES | ↓ | ↕ | – | ↓ | Saar et al. (2017) |
Managed livestock grazing | MPDSES | ↓ | ↑ (4 × 10–4) | – | ↕ (1 – 340) | ||
Riparian plant communities | Clearcutting | FDivS | ↓ | ↑ (10–4) | – | ↑ (0.04) | Biswas et al. (2016) |
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↑ | – | ↓ | |||
Wildfire | FDivS | ↓ | ↑ | – | ↑ | ||
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↓ | – | ↓ | |||
Semi-arid grassland | Sheep grazing | FRicSES | ↓ | – | – | ↓ (0.04) | Laliberté et al. (2013) |
FDisSES | – | ↓ (10–4) | – | – | |||
Semi-deciduous forest | Logging and fire | Rao | – | ↕ (0.5) | – | ↑ (10) | Réjou-Méchain et al. (2014) |
Semi-natural coastal grasslands | Land-use change | FDiv | ↑ | ↓ (2.5 × 10–3) | – | ↓ | Lewis et al. (2014) ‡ |
FRic | ↓ | ↑ | – | ↓ | |||
Sub-alpine meadow | Landslides | Filling proportion | ↓ | ↑ (2.5 × 10–5) | ↑ (1.6 × 10–3) | – | Smith et al. (2013) † |
Range | ↓ | ↓ | ↓ | – | |||
Sub-tropical floodplain lakes | Flooding –Ivinhema sub-basin | MPD | ↕ | ↕ | – | ↕ | Dunck et al. (2016)* |
Flooding –Paraná sub-basin | MPD | ↕ | ↑ | – | ↕ | ||
Temperate grasslands | Livestock grazing | Mantel correlations | ↓ | ↑ (10–6) | ↓ (2.5 × 10–5) | ↓ (0.02 – 11.63) | de Bello et al. (2013) |
Therophytic Mediterranean island | Goat grazing | FDivSES | – | ↑ | ↑ | – | Karadimou et al. (2015) † |
FEveSES | – | ↑ | ↑ | – | |||
FRicSES | – | ↓ | ↓ | – | |||
Tropical forest | Clearcutting | PwSES | ↓ | – | – | ↓ (0.04) | Yang et al. (2014) |
Tropical montane rain forests | Logging on adult trees | FDisSES response traits | ↕ | ↑ | ↓ | ↕ | Ding et al. (2012) |
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on saplings | FDisSES response traits | ↓ | ↕ (0.01) | ↓ (0.04) | ↓ (0.25) | ||
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on treelets | FDisSES response traits | ↓ | ↓ | ↓ | ↓ | ||
FDisSES effect traits | ↓ | ↓ | ↓ | ↓ | |||
Shifting cultivation on adult trees | FDisSES response traits | ↑ | ↑ | ↑ | ↑ | ||
FDisSES effect traits | ↓ | ↑ | ↑ | ↕ | |||
Shifting cultivation on saplings | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↓ | ↑ | ↓ | ↓ | |||
Shifting cultivation on treelets | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↕ | ↓ | ↕ | ↓ | |||
Tropical montane rain forest | Logging | FDisSES | ↓ | ↑ (0.01) | ↕ (0.04) | ↑ (0.25) | Ding et al. (2019) |
FRicSES | ↓ | ↑ | ↑ | ↑ | |||
Woody Mediterranean island | Goat grazing | FDiv | ↑ | ↑ (10–4) | ↑ (6.4 × 10–3) | – | Karadimou et al. (2015) † |
FEve | ↑ | ↕ | ↕ | – | |||
FRic | ↕ | ↑ | ↑ | – | |||
Percentage of cases supporting the model | 74.3 % | 60.5 % | 25 % | 51.6 % |
Ecosystem type . | Disturbance type . | Functional metric . | Increased spatial scale . | Effect of disturbance scale (ha) . | Reference . | ||
---|---|---|---|---|---|---|---|
. | . | . | . | Small/fine . | Intermediate . | Large . | . |
Arid shrubland | Rodent burrowing | FDisSES | ↓ | ↑ (10–4) | ↕ (0.01) | ↓ (0.25) | Current study |
Grasslands | Developing habitat (e.g. road verges and old fields) | MPDSES | ↓ | ↕ | – | ↓ | Saar et al. (2017) |
Managed livestock grazing | MPDSES | ↓ | ↑ (4 × 10–4) | – | ↕ (1 – 340) | ||
Riparian plant communities | Clearcutting | FDivS | ↓ | ↑ (10–4) | – | ↑ (0.04) | Biswas et al. (2016) |
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↑ | – | ↓ | |||
Wildfire | FDivS | ↓ | ↑ | – | ↑ | ||
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↓ | – | ↓ | |||
Semi-arid grassland | Sheep grazing | FRicSES | ↓ | – | – | ↓ (0.04) | Laliberté et al. (2013) |
FDisSES | – | ↓ (10–4) | – | – | |||
Semi-deciduous forest | Logging and fire | Rao | – | ↕ (0.5) | – | ↑ (10) | Réjou-Méchain et al. (2014) |
Semi-natural coastal grasslands | Land-use change | FDiv | ↑ | ↓ (2.5 × 10–3) | – | ↓ | Lewis et al. (2014) ‡ |
FRic | ↓ | ↑ | – | ↓ | |||
Sub-alpine meadow | Landslides | Filling proportion | ↓ | ↑ (2.5 × 10–5) | ↑ (1.6 × 10–3) | – | Smith et al. (2013) † |
Range | ↓ | ↓ | ↓ | – | |||
Sub-tropical floodplain lakes | Flooding –Ivinhema sub-basin | MPD | ↕ | ↕ | – | ↕ | Dunck et al. (2016)* |
Flooding –Paraná sub-basin | MPD | ↕ | ↑ | – | ↕ | ||
Temperate grasslands | Livestock grazing | Mantel correlations | ↓ | ↑ (10–6) | ↓ (2.5 × 10–5) | ↓ (0.02 – 11.63) | de Bello et al. (2013) |
Therophytic Mediterranean island | Goat grazing | FDivSES | – | ↑ | ↑ | – | Karadimou et al. (2015) † |
FEveSES | – | ↑ | ↑ | – | |||
FRicSES | – | ↓ | ↓ | – | |||
Tropical forest | Clearcutting | PwSES | ↓ | – | – | ↓ (0.04) | Yang et al. (2014) |
Tropical montane rain forests | Logging on adult trees | FDisSES response traits | ↕ | ↑ | ↓ | ↕ | Ding et al. (2012) |
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on saplings | FDisSES response traits | ↓ | ↕ (0.01) | ↓ (0.04) | ↓ (0.25) | ||
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on treelets | FDisSES response traits | ↓ | ↓ | ↓ | ↓ | ||
FDisSES effect traits | ↓ | ↓ | ↓ | ↓ | |||
Shifting cultivation on adult trees | FDisSES response traits | ↑ | ↑ | ↑ | ↑ | ||
FDisSES effect traits | ↓ | ↑ | ↑ | ↕ | |||
Shifting cultivation on saplings | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↓ | ↑ | ↓ | ↓ | |||
Shifting cultivation on treelets | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↕ | ↓ | ↕ | ↓ | |||
Tropical montane rain forest | Logging | FDisSES | ↓ | ↑ (0.01) | ↕ (0.04) | ↑ (0.25) | Ding et al. (2019) |
FRicSES | ↓ | ↑ | ↑ | ↑ | |||
Woody Mediterranean island | Goat grazing | FDiv | ↑ | ↑ (10–4) | ↑ (6.4 × 10–3) | – | Karadimou et al. (2015) † |
FEve | ↑ | ↕ | ↕ | – | |||
FRic | ↕ | ↑ | ↑ | – | |||
Percentage of cases supporting the model | 74.3 % | 60.5 % | 25 % | 51.6 % |
(↓) increased trait convergence, (↕) no difference among treatments, (↑) increased trait divergence and (–) pattern not tested. Expected patterns according to the conceptual model: (↓) as spatial scale increases, (↑) following disturbance at small/fine scale scales, (↕) following disturbance at intermediate scales and (↓) following disturbance at large scales. Definition and meaning of the different functional metrics are provided in Supplementary data Table S3
*Single lakes and river floodplain were defined as the small and large scales, respectively.
†The authors acknowledge that the scale used might not be sufficient to detect habitat filtering.
‡Whole study area (‘National’) was defined as the large scale.
Summary of studies addressing the effects of disturbance on functional dispersion metrics across spatial scales
Ecosystem type . | Disturbance type . | Functional metric . | Increased spatial scale . | Effect of disturbance scale (ha) . | Reference . | ||
---|---|---|---|---|---|---|---|
. | . | . | . | Small/fine . | Intermediate . | Large . | . |
Arid shrubland | Rodent burrowing | FDisSES | ↓ | ↑ (10–4) | ↕ (0.01) | ↓ (0.25) | Current study |
Grasslands | Developing habitat (e.g. road verges and old fields) | MPDSES | ↓ | ↕ | – | ↓ | Saar et al. (2017) |
Managed livestock grazing | MPDSES | ↓ | ↑ (4 × 10–4) | – | ↕ (1 – 340) | ||
Riparian plant communities | Clearcutting | FDivS | ↓ | ↑ (10–4) | – | ↑ (0.04) | Biswas et al. (2016) |
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↑ | – | ↓ | |||
Wildfire | FDivS | ↓ | ↑ | – | ↑ | ||
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↓ | – | ↓ | |||
Semi-arid grassland | Sheep grazing | FRicSES | ↓ | – | – | ↓ (0.04) | Laliberté et al. (2013) |
FDisSES | – | ↓ (10–4) | – | – | |||
Semi-deciduous forest | Logging and fire | Rao | – | ↕ (0.5) | – | ↑ (10) | Réjou-Méchain et al. (2014) |
Semi-natural coastal grasslands | Land-use change | FDiv | ↑ | ↓ (2.5 × 10–3) | – | ↓ | Lewis et al. (2014) ‡ |
FRic | ↓ | ↑ | – | ↓ | |||
Sub-alpine meadow | Landslides | Filling proportion | ↓ | ↑ (2.5 × 10–5) | ↑ (1.6 × 10–3) | – | Smith et al. (2013) † |
Range | ↓ | ↓ | ↓ | – | |||
Sub-tropical floodplain lakes | Flooding –Ivinhema sub-basin | MPD | ↕ | ↕ | – | ↕ | Dunck et al. (2016)* |
Flooding –Paraná sub-basin | MPD | ↕ | ↑ | – | ↕ | ||
Temperate grasslands | Livestock grazing | Mantel correlations | ↓ | ↑ (10–6) | ↓ (2.5 × 10–5) | ↓ (0.02 – 11.63) | de Bello et al. (2013) |
Therophytic Mediterranean island | Goat grazing | FDivSES | – | ↑ | ↑ | – | Karadimou et al. (2015) † |
FEveSES | – | ↑ | ↑ | – | |||
FRicSES | – | ↓ | ↓ | – | |||
Tropical forest | Clearcutting | PwSES | ↓ | – | – | ↓ (0.04) | Yang et al. (2014) |
Tropical montane rain forests | Logging on adult trees | FDisSES response traits | ↕ | ↑ | ↓ | ↕ | Ding et al. (2012) |
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on saplings | FDisSES response traits | ↓ | ↕ (0.01) | ↓ (0.04) | ↓ (0.25) | ||
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on treelets | FDisSES response traits | ↓ | ↓ | ↓ | ↓ | ||
FDisSES effect traits | ↓ | ↓ | ↓ | ↓ | |||
Shifting cultivation on adult trees | FDisSES response traits | ↑ | ↑ | ↑ | ↑ | ||
FDisSES effect traits | ↓ | ↑ | ↑ | ↕ | |||
Shifting cultivation on saplings | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↓ | ↑ | ↓ | ↓ | |||
Shifting cultivation on treelets | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↕ | ↓ | ↕ | ↓ | |||
Tropical montane rain forest | Logging | FDisSES | ↓ | ↑ (0.01) | ↕ (0.04) | ↑ (0.25) | Ding et al. (2019) |
FRicSES | ↓ | ↑ | ↑ | ↑ | |||
Woody Mediterranean island | Goat grazing | FDiv | ↑ | ↑ (10–4) | ↑ (6.4 × 10–3) | – | Karadimou et al. (2015) † |
FEve | ↑ | ↕ | ↕ | – | |||
FRic | ↕ | ↑ | ↑ | – | |||
Percentage of cases supporting the model | 74.3 % | 60.5 % | 25 % | 51.6 % |
Ecosystem type . | Disturbance type . | Functional metric . | Increased spatial scale . | Effect of disturbance scale (ha) . | Reference . | ||
---|---|---|---|---|---|---|---|
. | . | . | . | Small/fine . | Intermediate . | Large . | . |
Arid shrubland | Rodent burrowing | FDisSES | ↓ | ↑ (10–4) | ↕ (0.01) | ↓ (0.25) | Current study |
Grasslands | Developing habitat (e.g. road verges and old fields) | MPDSES | ↓ | ↕ | – | ↓ | Saar et al. (2017) |
Managed livestock grazing | MPDSES | ↓ | ↑ (4 × 10–4) | – | ↕ (1 – 340) | ||
Riparian plant communities | Clearcutting | FDivS | ↓ | ↑ (10–4) | – | ↑ (0.04) | Biswas et al. (2016) |
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↑ | – | ↓ | |||
Wildfire | FDivS | ↓ | ↑ | – | ↑ | ||
FRicS | ↓ | ↑ | – | ↑ | |||
FEveS | ↓ | ↓ | – | ↓ | |||
Semi-arid grassland | Sheep grazing | FRicSES | ↓ | – | – | ↓ (0.04) | Laliberté et al. (2013) |
FDisSES | – | ↓ (10–4) | – | – | |||
Semi-deciduous forest | Logging and fire | Rao | – | ↕ (0.5) | – | ↑ (10) | Réjou-Méchain et al. (2014) |
Semi-natural coastal grasslands | Land-use change | FDiv | ↑ | ↓ (2.5 × 10–3) | – | ↓ | Lewis et al. (2014) ‡ |
FRic | ↓ | ↑ | – | ↓ | |||
Sub-alpine meadow | Landslides | Filling proportion | ↓ | ↑ (2.5 × 10–5) | ↑ (1.6 × 10–3) | – | Smith et al. (2013) † |
Range | ↓ | ↓ | ↓ | – | |||
Sub-tropical floodplain lakes | Flooding –Ivinhema sub-basin | MPD | ↕ | ↕ | – | ↕ | Dunck et al. (2016)* |
Flooding –Paraná sub-basin | MPD | ↕ | ↑ | – | ↕ | ||
Temperate grasslands | Livestock grazing | Mantel correlations | ↓ | ↑ (10–6) | ↓ (2.5 × 10–5) | ↓ (0.02 – 11.63) | de Bello et al. (2013) |
Therophytic Mediterranean island | Goat grazing | FDivSES | – | ↑ | ↑ | – | Karadimou et al. (2015) † |
FEveSES | – | ↑ | ↑ | – | |||
FRicSES | – | ↓ | ↓ | – | |||
Tropical forest | Clearcutting | PwSES | ↓ | – | – | ↓ (0.04) | Yang et al. (2014) |
Tropical montane rain forests | Logging on adult trees | FDisSES response traits | ↕ | ↑ | ↓ | ↕ | Ding et al. (2012) |
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on saplings | FDisSES response traits | ↓ | ↕ (0.01) | ↓ (0.04) | ↓ (0.25) | ||
FDisSES effect traits | ↓ | ↕ | ↓ | ↓ | |||
Logging on treelets | FDisSES response traits | ↓ | ↓ | ↓ | ↓ | ||
FDisSES effect traits | ↓ | ↓ | ↓ | ↓ | |||
Shifting cultivation on adult trees | FDisSES response traits | ↑ | ↑ | ↑ | ↑ | ||
FDisSES effect traits | ↓ | ↑ | ↑ | ↕ | |||
Shifting cultivation on saplings | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↓ | ↑ | ↓ | ↓ | |||
Shifting cultivation on treelets | FDisSES response traits | ↓ | ↑ | ↕ | ↕ | ||
FDisSES effect traits | ↕ | ↓ | ↕ | ↓ | |||
Tropical montane rain forest | Logging | FDisSES | ↓ | ↑ (0.01) | ↕ (0.04) | ↑ (0.25) | Ding et al. (2019) |
FRicSES | ↓ | ↑ | ↑ | ↑ | |||
Woody Mediterranean island | Goat grazing | FDiv | ↑ | ↑ (10–4) | ↑ (6.4 × 10–3) | – | Karadimou et al. (2015) † |
FEve | ↑ | ↕ | ↕ | – | |||
FRic | ↕ | ↑ | ↑ | – | |||
Percentage of cases supporting the model | 74.3 % | 60.5 % | 25 % | 51.6 % |
(↓) increased trait convergence, (↕) no difference among treatments, (↑) increased trait divergence and (–) pattern not tested. Expected patterns according to the conceptual model: (↓) as spatial scale increases, (↑) following disturbance at small/fine scale scales, (↕) following disturbance at intermediate scales and (↓) following disturbance at large scales. Definition and meaning of the different functional metrics are provided in Supplementary data Table S3
*Single lakes and river floodplain were defined as the small and large scales, respectively.
†The authors acknowledge that the scale used might not be sufficient to detect habitat filtering.
‡Whole study area (‘National’) was defined as the large scale.
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