EntryID | ID | Author | Year | Forest Type | Paper Type | Metric Measured | Modeling Approach | Variance Explained | Driver Name | Value | Effect | Significance | Drivers Not Included |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
28-22 | 28 | Andrus | 2,022 | Mixed Conifer | Structural | Seedling / Sapling Precense | correlation | 0.54 | climate moisture deficit | Positive | Conditional | Standardized Precipitation Evaporation Index, heat load index, burn severity, forbes (%), shrubs (%) | |
28-21 | 28 | Andrus | 2,022 | Mixed Conifer | Structural | Stem Density | Generalized Linear Models | 0.84 | distance to edge | -0.48600 | Negative | high (P <0.01) | Standardized Precipitation Evaporation Index, heat load index, burn severity, forbes (%), shrubs (%) |
28-21 | % grass | -0.64200 | Negative | very high (P < 0.001) | |||||||||
28-21 | beers transformed aspect | -0.43090 | Negative | Not ( P > 0.05) | |||||||||
28-21 | salvage logging | 0.22780 | Positive | Not ( P > 0.05) | |||||||||
28-21 | random effect (year) | 0.60400 | Positive | very high (P < 0.001) | |||||||||
28-93 | 28 | Andrus | 2,022 | Ponderosa Pine | Structural | Stem Density | Generalized Linear Models | 0.789 | distance to edge | -0.37430 | Positive | Not ( P > 0.05) | Standardized Precipitation Evaporation Index, heat load index, burn severity, forbs (%), shrubs (%) |
28-93 | % grass | -0.40230 | Negative | high (P <0.01) | |||||||||
28-93 | beers aspect | -0.32960 | Positive | Not ( P > 0.05) | |||||||||
28-93 | salvage logging | 0.59170 | Positive | Not ( P > 0.05) | |||||||||
28-93 | random effect (year) | 0.62350 | Positive | very high (P < 0.001) | |||||||||
28-94 | 28 | Andrus | 2,022 | Douglas fir | Structural | Stem Density | Generalized Linear Models | 0.84 | distance to edge | -0.58850 | Negative | very high (P < 0.001) | Standardized Precipitation Evaporation Index, heat load index, burn severity, forbs (%), shrubs (%) |
28-94 | % grass | -0.31750 | Negative | high (P <0.01) | |||||||||
28-94 | beers aspect | -0.45320 | Negative | high (P <0.01) | |||||||||
28-94 | salvage logging | 0.36430 | Positive | Not ( P > 0.05) | |||||||||
28-94 | random effect (year) | 0.32900 | Positive | moderately ( P < 0.05) | |||||||||
28-95 | 28 | Andrus | 2,022 | Grand fir | Structural | Stem Density | Generalized Linear Models | 0.913 | distance to edge | -0.62210 | Negative | moderately ( P < 0.05) | Standardized Precipitation Evaporation Index, heat load index, burn severity, forbs (%), shrubs (%) |
28-95 | % grass | -0.46570 | Negative | high (P <0.01) | |||||||||
28-95 | beers aspect | -0.46030 | Positive | Not ( P > 0.05) | |||||||||
28-95 | salvage logging | 0.35700 | Positive | Not ( P > 0.05) | |||||||||
28-95 | random effect (year) | 0.27570 | Positive | Not ( P > 0.05) | |||||||||
4037-156 | 4037 | Aspinall | 2,025 | Lodgepole | Spectral | Stem Density, Biomass | Rank Test | 0.37 | vwc | -0.37000 | Negative | very high (P < 0.001) | |
4037-156 | biomass | -0.35000 | Negative | very high (P < 0.001) | |||||||||
4037-156 | soil bulk density | 0.24000 | Positive | high (P <0.01) | |||||||||
11-17 | 11 | Boag | 2,020 | Mixed Conifer | Structural | Seedling / Sapling Precense | Generalized Linear Models | Not reported | hli | -1.25000 | Negative | very high (P < 0.001) | years since fire, dNBR, Normal CMD, Normal MAP, Normal MAT, Standardized precipitation Evapotranspiration Index, Elevation, Serotiny, Post-fire Basal Area, Bare soil %, litter type, woody debris type, graminoids cover % , forb cover % |
11-17 | distance to seed source | -0.98000 | Negative | very high (P < 0.001) | |||||||||
11-17 | canopy closure | 0.94000 | Positive | very high (P < 0.001) | |||||||||
11-17 | shrub % | 0.75000 | Positive | high (P <0.01) | |||||||||
11-17 | rock % | -0.51000 | Negative | moderately ( P < 0.05) | |||||||||
11-127 | 11 | Boag | 2,020 | Non-Serotinous Conifer | Structural | Seedling / Sapling Precense | Generalized Linear Models | Not reported | hli | -1.19000 | Negative | very high (P < 0.001) | years since fire, dNBR, Normal CMD, Normal MAP, Normal MAT, Standardized precipitation Evapotranspiration Index, Elevation, Serotiny, Post-fire Basal Area, Bare soil %, litter type, woody debris type, graminoids cover % , forb cover %, rock cover % |
11-127 | distance to seed source | -1.03000 | Negative | high (P <0.01) | |||||||||
11-127 | canopy closure (%) | 0.71000 | Positive | moderately ( P < 0.05) | |||||||||
11-127 | shrub cover (%) | 0.76000 | Positive | moderately ( P < 0.05) | |||||||||
11-128 | 11 | Boag | 2,020 | Ponderosa Pine | Structural | Seedling / Sapling Precense | Generalized Linear Models | Not reported | hli | -0.91000 | Negative | high (P <0.01) | years since fire, dNBR, Normal CMD, Normal MAP, Normal MAT, Standardized precipitation Evapotranspiration Index, Elevation, Post-fire Basal Area, Bare soil %, litter type, graminoids cover % , forb cover %, Canopy Closure |
11-128 | distance to seed source | -1.67000 | Negative | very high (P < 0.001) | |||||||||
11-128 | wood cover % | 0.60000 | Positive | moderately ( P < 0.05) | |||||||||
11-128 | shrub cover % | 0.76000 | Positive | high (P <0.01) | |||||||||
11-129 | 11 | Boag | 2,020 | Douglas Fir | Structural | Seedling / Sapling Precense | Generalized Linear Models | Not reported | 3-year post-fire standardized precipitation evapotranspiration index | 0.49000 | Positive | Not ( P > 0.05) | years since fire, dNBR, Normal CMD, Normal MAP, Normal MAT, Elevation, Serotiny, Bare soil %, litter type, woody debris type, graminoids cover % , forb cover % |
11-129 | elevation | 0.51000 | Positive | moderately ( P < 0.05) | |||||||||
11-129 | hli | -1.28000 | Negative | very high (P < 0.001) | |||||||||
11-129 | distance to seed source | -0.90000 | Negative | moderately ( P < 0.05) | |||||||||
11-129 | basal area (post-fire) | 0.78000 | Positive | high (P <0.01) | |||||||||
11-129 | rock cover % | -0.67000 | Negative | moderately ( P < 0.05) | |||||||||
1962-62 | 1962 | Bonnet | 2,005 | Ponderosa Pine | Structural | Relative Seedling Germination Success | Partial Least Squares | understory vegetation (%) | -0.06000 | Negative | moderately ( P < 0.05) | Vegetation 10-50 cm (0.003), rock % (0.005), Soil moisture (%) 0.006, Burned shrubs (0.007), Unburned trees < 10 m tall (0.0097). Aspect (0.0189), post-fire basal area (0.020), Average post-fire DBH (0.0213), Average post-fire tree height (0.0274), Burned trees < 10 m (0.031), Burned trees > 10 m (.0393), cryptogram % (0.0697) | |
1962-62 | proportion of vegetation < 10 cm | -0.05997 | Negative | moderately ( P < 0.05) | |||||||||
1962-62 | bare ground (%) | -0.04000 | Negative | moderately ( P < 0.05) | |||||||||
1962-62 | total ground cover | -0.03700 | Negative | moderately ( P < 0.05) | |||||||||
1962-62 | richness | -0.03400 | Negative | ||||||||||
1962-62 | unburned litter on soil | -0.03200 | Negative | ||||||||||
1962-62 | burned litter depth | -0.02700 | Negative | moderately ( P < 0.05) | |||||||||
1962-62 | soil temperature | -0.02200 | Negative | ||||||||||
1962-62 | cover 50-100 cm tall | -0.01000 | Negative | ||||||||||
1962-62 | bare unburned soil | -0.00300 | Positive | ||||||||||
1962-62 | coarse woody debris | -0.00300 | Negative | ||||||||||
1962-62 | treen density (live post-fire) | -0.00100 | Negative | ||||||||||
1962-62 | unburned trees <10 m tall | -0.00100 | Positive | ||||||||||
1962-62 | scorched litter depth | 0.13640 | Positive | ||||||||||
32-23 | 32 | Braziunas | 2,023 | Subalpine | Structural | Stem Density | Mixed Linear Models | 0.29 | fire interval | -0.74000 | Negative | high (P <0.01), very high (P < 0.01) | |
32-23 | fire interval | -0.74000 | Negative | high (P <0.01), very high (P < 0.01) | |||||||||
32-23 | normal cmd | 0.40000 | Positive | very high (P < 0.001) | |||||||||
32-23 | normal cmd | 0.40000 | Positive | very high (P < 0.001) | |||||||||
32-23 | distance to-edge : short interval fire | -0.28000 | Negative | Conditional | |||||||||
32-23 | climate water deficit normal: fire interval | -0.24000 | Negative | high (P <0.01) | |||||||||
32-23 | distance to unburned:fire interval (long) | 0.07000 | Positive | Not ( P > 0.05) | |||||||||
32-23 | anomalous vpd | 0.34000 | Positive | moderately ( P < 0.05) | |||||||||
3-15 | 3 | Bright | 2,019 | Ponderosa Pine | Spectral | Random Forest | 0.5 | pre-fire nbr | 0.90000 | Positive | Not ( P > 0.05) | ||
3-15 | dnbr | 0.30000 | Negative | moderately ( P < 0.05) | |||||||||
3-15 | anomaly annual precipitation | 0.90000 | Positive | high (P <0.01) | |||||||||
3-15 | anomalous summer precipitation | 0.70000 | Positive | high (P <0.01) | |||||||||
3-15 | anomalous winter precipitation | 0.80000 | Negative | moderately ( P < 0.05) | |||||||||
3-15 | anomalous mean annual temperature | 1.00000 | Positive | very high (P < 0.001) | |||||||||
3-15 | anomalous maximum summer temperature | 0.70000 | Positive | moderately ( P < 0.05) | |||||||||
3-15 | anomalous winter minimum temperature | 0.80000 | Positive | moderately ( P < 0.05) | |||||||||
3-15 | distance-to-edge | 0.10000 | Negative | moderately ( P < 0.05) | |||||||||
3-15 | concavity | 0.10000 | Not ( P > 0.05) | ||||||||||
3-15 | slope | 0.20000 | Not ( P > 0.05) | ||||||||||
3-15 | aspect | 0.10000 | Not ( P > 0.05) | ||||||||||
3-16 | 3 | Bright | 2,019 | Mixed conifer | Spectral | Random Forest | 0.4 | pre-fire nbr & dnbr | 1.00000 | Positive | Not ( P > 0.05) | ||
3-16 | dnbr | 0.50000 | Negative | moderately ( P < 0.05) | |||||||||
3-16 | anomaly annual precipitation | 0.80000 | Positive | ||||||||||
3-16 | anomalous summer precipitation | 0.70000 | Positive | high (P <0.01) | |||||||||
3-16 | anomalous winter precipitation | 0.80000 | Negative | moderately ( P < 0.05) | |||||||||
3-16 | anomalous mean annual temperature | 0.60000 | Positive | very high (P < 0.001) | |||||||||
3-16 | anomalous maximum summer temperature | 0.90000 | Positive | moderately ( P < 0.05) | |||||||||
3-16 | anomalous winter minimum temperature | 0.70000 | Positive | moderately ( P < 0.05) | |||||||||
3-16 | distance-to-edge | 0.10000 | Negative | moderately ( P < 0.05) | |||||||||
3-16 | concavity | 0.20000 | Not ( P > 0.05) | ||||||||||
3-16 | slope | 0.20000 | Not ( P > 0.05) | ||||||||||
3-16 | aspect | 0.10000 | Not ( P > 0.05) | ||||||||||
522-56 | 522 | Buma | 2,012 | Subalpine forest | Spectral | Stem Density | Generalized Linear Models | 0.18 | elevation | Negative | moderately ( P < 0.05) | elevation, transformed aspect | |
522-56 | aspect | Positive | Not ( P > 0.05) | ||||||||||
1128-59 | 1128 | Busby | 2,022 | Subalpine | Structural | Stem Density | Boosted Regression Trees | 0.5 | weighted distance to edge | 43.30000 | Positive | high (P <0.01) | anomalous CMD, patch live basal area, patch height, patch width, patch size |
1128-59 | wood cover (%) | 9.40000 | Positive | high (P <0.01) | |||||||||
1128-59 | understory cover (%) | 4.20000 | Negative | high (P <0.01) | |||||||||
1128-59 | slope | 2.40000 | Negative | moderately ( P < 0.05) | |||||||||
1128-59 | heat load insolation | 1.20000 | Positive | moderately ( P < 0.05) | |||||||||
1128-59 | normal cmd | 2.40000 | Negative | high (P <0.01) | |||||||||
1128-59 | normal cmd | 2.40000 | Negative | high (P <0.01) | |||||||||
1128-59 | years since fire | 0.50000 | Positive | moderately ( P < 0.05) | |||||||||
1128-59 | residual autocorrelation | 34.90000 | Positive | very high (P < 0.001) | |||||||||
1128-71 | 1128 | Busby | 2,022 | Subalpine (non-serotinous) | Structural | Stem Density | Boosted Regression Trees | 0.5 | weighted distance to edge | 56.50000 | Positive | high (P <0.01) | anomalous CMD, patch live basal area, patch height, patch width, patch size |
1128-71 | wood cover (%) | 23.90000 | Positive | high (P <0.01) | |||||||||
1128-71 | understory cover (%) | 2.00000 | Negative | high (P <0.01) | |||||||||
1128-71 | slope | 3.20000 | Negative | moderately ( P < 0.05) | |||||||||
1128-71 | heat load insolation | 1.80000 | Positive | moderately ( P < 0.05) | |||||||||
1128-71 | normal cmd | 5.40000 | Negative | high (P <0.01) | |||||||||
1128-71 | normal cmd | 5.40000 | Negative | high (P <0.01) | |||||||||
1128-71 | years since fire | 0.50000 | Positive | moderately ( P < 0.05) | |||||||||
1128-71 | residual autocorrelation | 34.90000 | Positive | very high (P < 0.001) | |||||||||
1128-72 | 1128 | Busby | 2,022 | Pinus Contorta (lodgepole pine) | Structural | Stem Density | Boosted Regression Trees | 0.5 | weighted distance to edge | 28.20000 | Positive | high (P <0.01) | anomalous CMD, patch live basal area, patch height, patch width, patch size |
1128-72 | wood cover (%) | 3.60000 | Negative | high (P <0.01) | |||||||||
1128-72 | understory cover (%) | 2.70000 | Positive | high (P <0.01) | |||||||||
1128-72 | slope | 7.30000 | Negative | moderately ( P < 0.05) | |||||||||
1128-72 | heat load insolation | 12.90000 | Positive | moderately ( P < 0.05) | |||||||||
1128-72 | normal cmd | 12.60000 | Positive | high (P <0.01) | |||||||||
1128-72 | normal cmd | 12.60000 | Positive | high (P <0.01) | |||||||||
1128-72 | years since fire | 0.50000 | Positive | moderately ( P < 0.05) | |||||||||
1128-72 | residual autocorrelation | 34.90000 | Positive | very high (P < 0.001) | |||||||||
1128-73 | 1128 | Busby | 2,022 | Mountain hemlock | Structural | Stem Density | Boosted Regression Trees | 0.5 | weighted distance to edge | 47.60000 | Positive | high (P <0.01) | anomalous CMD, patch live basal area, patch height, patch width, patch size |
1128-73 | wood cover (%) | 23.30000 | Positive | high (P <0.01) | |||||||||
1128-73 | understory cover (%) | 2.60000 | Negative | high (P <0.01) | |||||||||
1128-73 | slope | 1.80000 | Negative | moderately ( P < 0.05) | |||||||||
1128-73 | heat load insolation | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
1128-73 | normal cmd | 2.00000 | Negative | high (P <0.01) | |||||||||
1128-73 | normal cmd | 2.00000 | Negative | high (P <0.01) | |||||||||
1128-73 | years since fire | 0.60000 | Positive | moderately ( P < 0.05) | |||||||||
1128-73 | residual autocorrelation | 34.90000 | Positive | very high (P < 0.001) | |||||||||
1128-74 | 1128 | Busby | 2,022 | Mountain hemlock | Structural | Stem Density | Boosted Regression Trees | 0.5 | weighted distance to edge | 68.30000 | Positive | high (P <0.01) | anomalous CMD, patch live basal area, patch height, patch width, patch size |
1128-74 | wood cover (%) | 2.10000 | Positive | high (P <0.01) | |||||||||
1128-74 | understory cover (%) | 0.50000 | Negative | high (P <0.01) | |||||||||
1128-74 | slope | 1.20000 | Negative | moderately ( P < 0.05) | |||||||||
1128-74 | heat load insolation | 1.30000 | Positive | moderately ( P < 0.05) | |||||||||
1128-74 | normal cmd | 10.50000 | Negative | high (P <0.01) | |||||||||
1128-74 | normal cmd | 10.50000 | Negative | high (P <0.01) | |||||||||
1128-74 | years since fire | 2.30000 | Positive | moderately ( P < 0.05) | |||||||||
1128-74 | residual autocorrelation | 34.90000 | Positive | very high (P < 0.001) | |||||||||
439-55 | 439 | Celebrezze | 2,024 | Mixed Conifer | Structural | Composition | Generalized Linear Models | 0.86 | post-fire temperature | -3.16800 | Negative | Not ( P > 0.05) | Slope, heat load insolation, transformed aspect, post-fire maximum VPD |
439-55 | post-fire precipitation | 9.39300 | Positive | very high (P < 0.001) | |||||||||
439-55 | precipitation:temperature interaction | -6.57200 | Negative | very high (P < 0.001) | |||||||||
439-55 | elevation | -0.63420 | Negative | high (P <0.01) | |||||||||
439-55 | post-fire precipitation | -0.90530 | Negative | high (P <0.01) | |||||||||
439-54 | 439 | Celebrezze | 2,024 | Mixed Conifer | Structural | Stem Density | Generalized Linear Models | 0.71 | continuous heat-insolation load index | -0.20518 | Negative | Not ( P > 0.05) | Elevation, slope, post-fire temperature, post-fire VPD |
439-54 | transformed aspect | 0.02261 | Positive | Not ( P > 0.05) | |||||||||
439-54 | post-fire precipitation | 0.96517 | Positive | very high (P < 0.001) | |||||||||
439-54 | interaction aspect and heat load | 0.93084 | Negative | very high (P < 0.001) | |||||||||
85-35 | 85 | Clark-Wolf | 2,022 | Mixed-conifer forest | Structural | Seedling / Sapling Precense | Generalized Linear Models | 0.72 | basal area (lodgepole pine) | 1.03300 | Positive | very high (P < 0.001) | Year2, Year3, Year2 combined with PICO Basal Area, Year3 combined with PICO Basal Area. |
85-35 | distance-to-edge | -1.42500 | Negative | very high (P < 0.001) | |||||||||
85-35 | heat load index | -0.10600 | Positive | Not ( P > 0.05) | |||||||||
85-35 | annual precipitation | 0.23400 | Positive | Not ( P > 0.05) | |||||||||
85-35 | temperature annual | -0.65600 | Negative | moderately ( P < 0.05) | |||||||||
85-35 | overstory fire effects (axis1) | 0.67100 | Positive | moderately ( P < 0.05) | |||||||||
85-35 | forb cover | 0.60800 | Positive | very high (P < 0.001) | |||||||||
85-35 | soil nitrogen | -0.86100 | Negative | very high (P < 0.001) | |||||||||
85-35 | heat load index combined with precipitation | 0.68300 | Positive | very high (P < 0.001) | |||||||||
85-35 | heat load index combined with forb cover | 0.35500 | Positive | high (P <0.01) | |||||||||
85-36 | 85 | Clark-Wolf | 2,022 | Douglas Fir | Structural | Seedling / Sapling Precense | Generalized Linear Models | 0.52 | pre-fire composition | 1.43800 | Positive | moderately ( P < 0.05) | year2, year3 |
85-36 | distance-to-edge | -0.56500 | Negative | very high (P < 0.001) | |||||||||
85-36 | canopy | 0.57700 | Positive | very high (P < 0.001) | |||||||||
85-36 | understory conditions / cover (axis2) | -1.15500 | Negative | very high (P < 0.001) | |||||||||
85-37 | 85 | Clark-Wolf | 2,022 | Lodgepole Pine | Structural | Seedling / Sapling Precense | Generalized Linear Models | 0.77 | basal area (lodgepole pine) | 1.46400 | Positive | very high (P < 0.001) | year2, year3 |
85-37 | distance-to-edge | -0.49200 | Negative | high (P <0.01) | |||||||||
85-37 | heat load index | -0.72200 | Negative | very high (P < 0.001) | |||||||||
85-37 | climatic water deficit | -0.62200 | Negative | high (P <0.01) | |||||||||
85-37 | coarse woody debris cover | 0.67200 | Positive | very high (P < 0.001) | |||||||||
85-37 | soil nitrogen | -0.91200 | Negative | very high (P < 0.001) | |||||||||
85-37 | heat load index combined with climatic water deficit | -0.43500 | Negative | moderately ( P < 0.05) | |||||||||
85-38 | 85 | Clark-Wolf | 2,022 | Larch | Structural | Seedling / Sapling Precense | Generalized Linear Models | 0.71 | pre-fire composition | 2.17000 | Positive | high (P <0.01) | |
85-38 | bare ground cover | -1.94900 | Negative | very high (P < 0.001) | |||||||||
85-38 | pp_dwt (propagule pressure) | 1.72400 | Positive | very high (P < 0.001) | |||||||||
85-38 | overstory fire effects (axis1) | 1.47200 | Positive | moderately ( P < 0.05) | |||||||||
85-38 | maximum temperature | -0.72500 | Negative | moderately ( P < 0.05) | |||||||||
85-29 | 85 | Clark-Wolf | 2,022 | Mixed-conifer forest | Structural | Stem Density | Generalized Linear Models | 0.75 | distance-to-edge | -1.24600 | Negative | very high (P < 0.001) | distance to weighted live tree cover, basal area of focal species, TPI, normal annual precipitation, normal growing season precipitation, post-fire growing season precipitation, normal CMD, average summer temperature, dNBR, canopy cover (%), ground cover, nitrate, ammonium |
85-29 | basal area (pine) | 1.03200 | Positive | very high (P < 0.001) | |||||||||
85-29 | soil nitrogen | -0.77600 | Negative | very high (P < 0.001) | |||||||||
85-29 | understory burn severity | 0.72900 | Positive | very high (P < 0.001) | |||||||||
85-29 | overstory burn severity | 0.68500 | Positive | high (P <0.01) | |||||||||
85-29 | maximum summer temperature | -0.65700 | Negative | very high (P < 0.001) | |||||||||
85-32 | 85 | Clark-Wolf | 2,022 | Pseudotsuga menziezii | Structural | Stem Density | Generalized Linear Models | 0.56 | pre-fire composition | 2.03000 | Positive | very high (P < 0.001) | distance to weighted live tree cover, TPI, normal annual precipitation, normal growing season precipitation, post-fire growing season precipitation, normal CMD, average summer temperature, canopy cover (%), ground cover, nitrate, ammonium, overstory burn severity, soil nitrogen |
85-32 | maximum summer temperature | -1.05200 | Negative | very high (P < 0.001) | |||||||||
85-32 | understory burn severity | 0.91670 | Positive | very high (P < 0.001) | |||||||||
85-32 | dnbr | -0.60000 | Negative | high (P <0.01) | |||||||||
85-32 | pre-fire composition | 0.52020 | Positive | very high (P < 0.001) | |||||||||
85-33 | 85 | Clark-Wolf | 2,022 | Pinus Contorta (lodgepole pine) | Structural | Stem Density | Generalized Linear Models | 0.95 | pre-fire composition | 3.11090 | Positive | very high (P < 0.001) | normal annual precipitation, normal growing season precipitation, post-fire growing season precipitation, average summer temperature, canopy cover (%), nitrate, ammonium, overstory burn severity, soil nitrogen |
85-33 | basal area lodgepole | 0.74450 | Positive | very high (P < 0.001) | |||||||||
85-33 | weighted distance-to-edge | 0.74460 | Positive | very high (P < 0.001) | |||||||||
85-33 | wood cover (%) | 0.66530 | Positive | very high (P < 0.001) | |||||||||
85-33 | canopy cover (%) | 0.51620 | Positive | very high (P < 0.001) | |||||||||
85-33 | soil nitrogen | -0.48690 | Negative | high (P <0.01), very high (P < 0.01) | |||||||||
85-33 | tpi | -0.47890 | Negative | very high (P < 0.001) | |||||||||
85-33 | tpi | -0.47890 | Negative | very high (P < 0.001) | |||||||||
85-33 | normal cmd | -0.36290 | Negative | moderately ( P < 0.05) | |||||||||
85-33 | normal cmd | -0.36290 | Negative | moderately ( P < 0.05) | |||||||||
85-34 | 85 | Clark-Wolf | 2,022 | Larch | Structural | Stem Density | Generalized Linear Models | 0.74 | pre-fire composition | 2.30070 | Positive | very high (P < 0.001) | |
85-34 | weighted distance-to-edge | 0.78270 | Positive | very high (P < 0.001) | |||||||||
85-34 | nitrite | -0.94080 | Negative | high (P <0.01) | |||||||||
85-34 | understory burn severity | 0.93800 | Positive | very high (P < 0.001) | |||||||||
85-34 | maximum summer temperature | -0.67850 | Negative | high (P <0.01) | |||||||||
324-49 | 324 | Clason | 2,022 | Mixed Conifer | Structural | Live Carbon | Generalized Linear Models | 0.05 | no planting | -8.50000 | Negative | moderately ( P < 0.05) | |
324-49 | planting | -0.70000 | Positive | Not ( P > 0.05) | |||||||||
324-49 | time since fire | 1.30000 | Positive | moderately ( P < 0.05) | |||||||||
324-49 | growing degree days | 5.40000 | Not ( P > 0.05) | ||||||||||
324-49 | map | 3.80000 | Positive | Not ( P > 0.05) | |||||||||
324-49 | soil carbon:nitrogen ratio | 2.40000 | Positive | Not ( P > 0.05) | |||||||||
324-49 | coarse fragments % | Negative | moderately ( P < 0.05) | ||||||||||
324-49 | % clay | 3.50000 | Positive | Not ( P > 0.05) | |||||||||
324-49 | heat load index | Negative | high (P <0.01) | ||||||||||
324-49 | slope | Negative | Not ( P > 0.05) | ||||||||||
121-146 | 121 | Coop | 2,019 | Mixed Conifer | Structural | Stem Density | Generalized Linear Models | 0.9 | distance to edge | -0.00300 | Negative | high (P <0.01) | |
121-146 | refugia density | -0.07900 | Negative | very high (P < 0.001) | |||||||||
121-146 | site effect | 2.27000 | Positive | high (P <0.01) | |||||||||
139-2 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Composition | Principal coordinate analysis | 0.9 | heat load | Positive | |||
139-2 | burn severity | Negative | |||||||||||
139-2 | burn severity | Negative | |||||||||||
139-2 | burn severity | Negative | |||||||||||
139-2 | slope | Negative | |||||||||||
139-3 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Principal coordinate analysis | 0.9 | distance to edge | Positive | ||||
139-3 | site level warmth | Positive | |||||||||||
139-4 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Principal coordinate analysis | 0.9 | rdnbr | Positive | ||||
139-4 | distance to edge | Positive | |||||||||||
139-4 | site level warmth | Positive | |||||||||||
139-5 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Principal coordinate analysis | 0.9 | rdnbr | Positive | ||||
139-5 | distance to edge | Positive | |||||||||||
139-6 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Principal coordinate analysis | 0.9 | site level warmth | Positive | ||||
139-6 | distance to edge | Positive | |||||||||||
139-7 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Principal coordinate analysis | 0.9 | winter precipitation | Positive | ||||
139-7 | summer precipitation | Positive | |||||||||||
139-7 | slope | Positive | |||||||||||
139-8 | 139 | Coop | 2,023 | Dry Mixed Conifer | Structural | Principal coordinate analysis | 0.9 | site weather warmth | Negative | ||||
139-8 | rdnbr | Positive | |||||||||||
73-152 | 73 | Coop | 2,010 | Mixed Conifer | Structural | Stem Density | Generalized Linear Models | Not provided | burn severity | 1.65900 | Positive | very high (P < 0.001) | |
73-152 | burn severity | 1.65900 | Positive | very high (P < 0.001) | |||||||||
73-152 | burn severity | 1.65900 | Positive | very high (P < 0.001) | |||||||||
73-152 | distance to edge | -0.58700 | Negative | very high (P < 0.001) | |||||||||
73-152 | elevation | -0.00200 | Negative | very high (P < 0.001) | |||||||||
73-152 | aspect | Positive | Not ( P > 0.05) | ||||||||||
73-152 | slope | Positive | Not ( P > 0.05) | ||||||||||
73-173 | 73 | Coop | 2,010 | Subalpine fir | Structural | Stem Density | Generalized Linear Models | Not provided | burn severity | 1.92700 | Positive | high (P <0.01) | |
73-173 | burn severity | 1.92700 | Positive | high (P <0.01) | |||||||||
73-173 | burn severity | 1.92700 | Positive | high (P <0.01) | |||||||||
73-173 | distance to edge | -1.83700 | Negative | very high (P < 0.001) | |||||||||
73-173 | elevation | Not ( P > 0.05) | |||||||||||
73-173 | aspect | Not ( P > 0.05) | |||||||||||
73-173 | slope | Not ( P > 0.05) | |||||||||||
73-174 | 73 | Coop | 2,010 | Engelmann Spruce | Structural | Stem Density | Generalized Linear Models | Not provided | burn severity | 2.86200 | Positive | very high (P < 0.001) | |
73-174 | burn severity | 2.86200 | Positive | very high (P < 0.001) | |||||||||
73-174 | burn severity | 2.86200 | Positive | very high (P < 0.001) | |||||||||
73-174 | distance to edge | -1.37900 | Negative | very high (P < 0.001) | |||||||||
73-174 | elevation | Not ( P > 0.05) | |||||||||||
73-174 | aspect | Not ( P > 0.05) | |||||||||||
73-174 | slope | Not ( P > 0.05) | |||||||||||
73-175 | 73 | Coop | 2,010 | Lodgepole Pine | Structural | Stem Density | Generalized Linear Models | Not provided | burn severity | 4.81300 | Positive | very high (P < 0.001) | |
73-175 | burn severity | 4.81300 | Positive | very high (P < 0.001) | |||||||||
73-175 | burn severity | 4.81300 | Positive | very high (P < 0.001) | |||||||||
73-175 | distance to edge | -1.50500 | Negative | very high (P < 0.001) | |||||||||
73-175 | elevation | -0.00600 | Negative | very high (P < 0.001) | |||||||||
73-175 | aspect | Not ( P > 0.05) | |||||||||||
73-175 | slope | -0.02890 | Negative | moderately ( P < 0.05) | |||||||||
120-134 | 120 | Crockett | 2,024 | Ponderosa Pine, Mixed conifer, Sub-Alpine | Spectral | Random Forests | 0.743 | year 5 fire year precipitation | 18,588.62000 | Positive | very high (P < 0.001) | ||
120-134 | year of fire precipitation variability | 18,588.62000 | Positive | very high (P < 0.001) | |||||||||
120-134 | slope length factor (ls) | 2,405.37000 | Positive | very high (P < 0.001) | |||||||||
120-134 | k-factor (slope erodibility) | 6,687.82400 | Negative | very high (P < 0.001) | |||||||||
120-134 | year 5 vpd | 22,909.88000 | Positive | very high (P < 0.001) | |||||||||
120-134 | year 5 cwd | 21,833.36000 | Positive | very high (P < 0.001) | |||||||||
120-134 | year 5 total precipitation | 25,754.74000 | Positive | very high (P < 0.001) | |||||||||
120-134 | year 5 maximum temperature | 17,442.12000 | Positive | Conditional | |||||||||
120-134 | month of fire | 10,091.85000 | Negative | very high (P < 0.001) | |||||||||
46-137 | 46 | Davis | 2,019 | Ponderosa Pine | Structural | Seedling / Sapling Precense | Boosted Regression Trees | 0.79 | distance to seed source | 32.00000 | Negative | very high (P < 0.001) | shrub %, aspect, slope, litter %, forb %, anomalous AET, normal VWC, normal VPD, pre-fire density, anomalous maximum temperature, anomalous spring VWC |
46-137 | time since fire | 22.00000 | Negative | very high (P < 0.001) | |||||||||
46-137 | dnbr | 22.00000 | Negative | ||||||||||
46-137 | anomalous mean vwc | 13.00000 | Positive | very high (P < 0.001) | |||||||||
46-137 | anomalous mean summer bpd | 11.00000 | Negative | very high (P < 0.001) | |||||||||
46-166 | 46 | Davis | 2,019 | Pseudotsuga menziezii (Doug Fir), | Structural | Seedling / Sapling Precense | Boosted Regression Trees | 0.79 | distance to seed source | 30.00000 | Negative | very high (P < 0.001) | shrub %, aspect, slope, litter %, forb %, anomalous AET, normal VWC, normal VPD, pre-fire density, anomalous mean VPD |
46-166 | time since fire | 34.00000 | Negative | very high (P < 0.001) | |||||||||
46-166 | dnbr | 14.00000 | Negative | ||||||||||
46-166 | anomalous mean soil moisture | 23.00000 | Positive | very high (P < 0.001) | |||||||||
46-166 | anomalous maximum temperature | 13.00000 | Negative | very high (P < 0.001) | |||||||||
3888-65 | 3888 | Dodson | 2,013 | Mixed Conifer | Structural | Seedling / Sapling Precense | 0.862 | elevation | 0.00700 | Positive | very high (P < 0.001) | ||
2-14 | 2 | Downing | 2,019 | Mixed Conifer | Structural | Stem Density | Mixed Linear Models | Not reported | distance to edge | -0.00700 | Negative | high (P <0.01) | |
2-14 | patch density | 0.00200 | Positive | moderately ( P < 0.05) | |||||||||
2-14 | dnbr | 0.80000 | Positive | Not ( P > 0.05) | |||||||||
2-14 | elevation | 10.06000 | Positive | high (P <0.01) | |||||||||
2-14 | elevation (squared) | -12.15000 | Positive | very high (P < 0.001) | |||||||||
2-14 | post-fire cmd | 0.75000 | Positive | Not ( P > 0.05) | |||||||||
2-14 | post-fire cmd quadratic | 10.52000 | Positive | very high (P < 0.001) | |||||||||
2-14 | heat load insolation | 0.18000 | Positive | Not ( P > 0.05) | |||||||||
2-14 | shrub cover | -0.00500 | Positive | Not ( P > 0.05) | |||||||||
2-14 | pre-fire basal area | -0.00100 | Positive | Not ( P > 0.05) | |||||||||
2-91 | 2 | Downing | 2,019 | Ponderosa Pine | Structural | Stem Density | Mixed Linear Models | Not reported | distance to edge | -0.00400 | Negative | very high (P < 0.001) | |
2-91 | refugia density | -0.00300 | Negative | high (P <0.01) | |||||||||
2-91 | dnbr | 0.00200 | Positive | Not ( P > 0.05) | |||||||||
2-91 | elevation | 3.77000 | Positive | Not ( P > 0.05) | |||||||||
2-91 | elevation squared | -9.96000 | Negative | very high (P < 0.001) | |||||||||
2-91 | cmd | 10.34000 | Negative | very high (P < 0.001) | |||||||||
2-91 | cmd squared | 7.58000 | Negative | high (P <0.01) | |||||||||
2-91 | heat load | 0.59000 | Positive | Not ( P > 0.05) | |||||||||
2-91 | pre-fire basal area | 0.00300 | Positive | Not ( P > 0.05) | |||||||||
2-91 | % shrub | 0.01300 | Positive | high (P <0.01) | |||||||||
2-92 | 2 | Downing | 2,019 | Douglas fir | Structural | Stem Density | Mixed Linear Models | distance to edge | -0.00700 | Negative | high (P <0.01) | ||
2-92 | refugia density | -0.00400 | Negative | very high (P < 0.001) | |||||||||
2-92 | dnbr | 0.00300 | Positive | high (P <0.01) | |||||||||
2-92 | elevation | 0.36000 | Positive | Not ( P > 0.05) | |||||||||
2-92 | elevation squared | -8.37000 | Negative | high (P <0.01) | |||||||||
2-92 | cmd | 0.79000 | Negative | very high (P < 0.001) | |||||||||
2-92 | cmd squared | 8.47000 | Negative | very high (P < 0.001) | |||||||||
2-92 | heat load | -3.69000 | Negative | very high (P < 0.001) | |||||||||
2-92 | pre-fire basal area | 0.00700 | Positive | Not ( P > 0.05) | |||||||||
2-92 | % shrub | 0.03200 | Positive | Not ( P > 0.05) | |||||||||
61-97 | 61 | Guz | 2,022 | Mixed Conifer | Spectral | Random Forests | 0.1812 | elevation | Positive | Fire History, soil type, depth to bedrock, soil composition, site-level drainage | |||
61-97 | slope | Negative | |||||||||||
61-97 | aspect | Negative | |||||||||||
61-98 | 61 | Guz | 2,022 | Mixed Conifer | Spectral | Random Forests | 0.49 | anomalous winter precipitation | -0.03000 | Negative | very high (P < 0.001) | ||
61-99 | 61 | Guz | 2,022 | Mixed Conifer | Spectral | Random Forests | 0.87 | anomalous winter maximum temperature | -0.60000 | Negative | high (P <0.01) | ||
61-99 | anomalous winter mean temperature | -1.02000 | Negative | very high (P < 0.001) | |||||||||
61-100 | 61 | Guz | 2,022 | Mixed Conifer | Spectral | Random Forests | 0.65 | anomalous winter minimum temperature | 0.58000 | Positive | very high (P < 0.001) | ||
150-44 | 150 | Haire | 2,010 | Ponderosa Pine | Structural | Stem Density | Generalized Linear Models | 0.78 | kernel distance | Positive | high (P <0.01) | aspen cover, heat load, forb cover %, neighborhood fire severity | |
150-44 | ground cover % | Positive | very high (P < 0.001) | ||||||||||
150-44 | elevation | Positive | very high (P < 0.001) | ||||||||||
150-44 | twi | Positive | very high (P < 0.001) | ||||||||||
150-44 | reburn | Negative | very high (P < 0.001) | ||||||||||
8-136 | 8 | Hammond | 2,021 | Ponderosa Pine | Structural | Stem Density | Non-Parametric Multiplicative Regression | 0.39 | post-fire woody fuels | 0.03700 | Positive | very high (P < 0.001) | Post-fire mean maximum summer temperature, post-fire mean maximum fall temperature, post-fire winter precipitation, post-fire fall precipitation, post-fire fall growing days, post-fire winter PAS, post-fire spring PAS, post-fire fall PAS, post-fire winter AET, post-fire fall AET, post-fire spring AETI, post-fire winter RH, post-fire spring RH, post-fire summer RH, elevation, aspect, slope, dNBR, soil productivity, distance to seed-source, understory richness, understory cover %, rock %, soil %, char %, tall shrub %, litter depth, post-fire live BA, post-fire dead BA |
8-136 | cwd | 0.03000 | Positive | very high (P < 0.001) | |||||||||
8-136 | litter depth | 0.11400 | Positive | very high (P < 0.001) | |||||||||
8-136 | post-fire fall precipitation | 0.03500 | Positive | very high (P < 0.001) | |||||||||
16-133 | 16 | Harvey | 2,016 | Structural | Stem Density | Generalized Linear Models | 0.72 | region | -1.17000 | Negative | high (P <0.01) | Distance to live tree, distance to edge, RdNBR, pre-fire stems, slope, shrub % | |
16-133 | anomalous growing season cmd | -0.62000 | Negative | high (P <0.01) | |||||||||
16-133 | aspect | -0.21000 | Negative | moderately ( P < 0.05) | |||||||||
16-133 | distance to seed | -1.39000 | Negative | very high (P < 0.001) | |||||||||
16-159 | 16 | Harvey | 2,016 | Serotinous Lodgepole | Structural | Generalized Linear Models | 0.79 | pre-fire stem density | 0.40000 | Positive | moderately ( P < 0.05) | Region, Anomalous Growing season CMD, Beers Aspect, Distance to seed source, distance to edge, distance to live tree, pre-fire tree presence, RdNBR | |
16-159 | slope (%) | 0.63000 | Positive | very high (P < 0.001) | |||||||||
16-160 | 16 | Harvey | 2,016 | Non-Serotinous Lodgepole Pine | Structural | Generalized Linear Models | 0.67 | region | -0.67000 | Negative | high (P <0.01) | Anomalous Growing season CMD, Slope, Beers Aspect, Distance to edge, distance to live tree, RdNBR, Shrub %, pre-fire presence | |
16-160 | distance to seed source | -0.56000 | Negative | high (P <0.01) | |||||||||
16-160 | pre-fire stem density | 0.91000 | Positive | very high (P < 0.001) | |||||||||
16-161 | 16 | Harvey | 2,016 | Engelmann Spruce | Structural | Generalized Linear Models | 0.91 | region | -2.09000 | Negative | very high (P < 0.001) | Distance to edge, distance to live tree, Shrub %, pre-fire presence | |
16-161 | anomalous growing season cmd | -1.19000 | Negative | very high (P < 0.001) | |||||||||
16-161 | beers aspect | -0.38000 | Positive | high (P <0.01) | |||||||||
16-161 | distance to seed source | -2.73000 | Negative | very high (P < 0.001) | |||||||||
16-161 | pre-fire stem density | 0.78000 | Positive | high (P <0.01) | |||||||||
16-161 | slope | -0.41200 | Negative | high (P <0.01) | |||||||||
16-162 | 16 | Harvey | 2,016 | Subalpine Fir | Structural | Generalized Linear Models | 0.38 | region | -1.11000 | Negative | very high (P < 0.001) | Slope, Beers Aspect, Distance to edge, distance to live tree, RdNBR, Shrub %, pre-fire presence | |
16-162 | anomalous growing season cmd | -0.74000 | Negative | high (P <0.01) | |||||||||
16-162 | distance to seed source | -2.11000 | Negative | high (P <0.01) | |||||||||
16-162 | pre-fire stem density | 0.57000 | Positive | high (P <0.01) | |||||||||
16-163 | 16 | Harvey | 2,016 | Larch | Structural | Generalized Linear Models | 0.73 | slope | 0.48000 | Positive | very high (P < 0.001) | Anomalous Growing season CMD, Beers Aspect, Distance to edge, distance to live tree, RdNBR, Shrub %, pre-fire presence, pre-fire stem density, Region, distance to seed source | |
16-164 | 16 | Harvey | 2,016 | Douglas-Fir | Structural | Generalized Linear Models | 0.47 | slope | 0.62000 | Positive | very high (P < 0.001) | Anomalous Growing season CMD, Beers Aspect, Distance to edge, distance to live tree, RdNBR, Shrub %, pre-fire presence, pre-fire stem density, Region, distance to seed source | |
16-165 | 16 | Harvey | 2,016 | Whitebark Pine | Structural | Generalized Linear Models | 0.28 | beers aspect | -0.42000 | Positive | very high (P < 0.001) | Anomalous Growing season CMD, Slope, Distance to edge, distance to live tree, RdNBR, Shrub %, pre-fire presence, pre-fire stem density, Region, distance to seed source | |
1737-11 | 1737 | Harvey | 2,013 | Douglas Fir | Structural | Stem Density | Random Forest | Not Reported | beetle-killed basal area | -4.31000 | Negative | high (P <0.01) | pre-fire live and dead basal area, total douglas-fir pre-fire basal area, elevation, slope, aspect, TPI, slope, TWI, distance to seed source |
1737-11 | fire severity | -0.48000 | Negative | moderately ( P < 0.05) | |||||||||
406-139 | 406 | Hoecker | 2,022 | Engelmann Spruce | Structural | Stem Density | Generalized Linear Models | 0.25 | pre-fire basal area | 4.04000 | Positive | Not ( P > 0.05) | Growing season maximum temperature |
406-139 | distance to low-severity | -8.92000 | Negative | moderately ( P < 0.05) | |||||||||
406-139 | post-fire vpd | -1.80000 | Negative | Not ( P > 0.05) | |||||||||
406-139 | aspect | -2.46000 | Negative | moderately ( P < 0.05) | |||||||||
406-139 | soil organic material | -7.27000 | Negative | moderately ( P < 0.05) | |||||||||
406-139 | clay % | 0.24000 | Positive | Not ( P > 0.05) | |||||||||
406-167 | 406 | Hoecker | 2,022 | Subalpine Fir | Structural | Stem Density | Generalized Linear Models | 0.32 | pre-fire ba | 2.82000 | Positive | moderately ( P < 0.05) | Growing season maximum temperature |
406-167 | distance to low severity | -8.84000 | Negative | Not ( P > 0.05) | |||||||||
406-167 | post-fire vpd | -4.32000 | Negative | Not ( P > 0.05) | |||||||||
406-167 | aspect | -2.45000 | Negative | moderately ( P < 0.05) | |||||||||
406-167 | soil organic material | 0.84000 | Positive | Not ( P > 0.05) | |||||||||
406-167 | clay % | -1.30000 | Negative | Not ( P > 0.05) | |||||||||
406-168 | 406 | Hoecker | 2,022 | Lodgepole Pine | Structural | Stem Density | Generalized Linear Models | 0.32 | serotiny | 2.34000 | Positive | very high (P < 0.001) | Growing season maximum temperature |
406-168 | distance to low severity | 0.27000 | Positive | Not ( P > 0.05) | |||||||||
406-168 | post-fire vpd | 0.06000 | Positive | Not ( P > 0.05) | |||||||||
406-168 | aspect | -0.30000 | Positive | Not ( P > 0.05) | |||||||||
406-168 | soil organic material | -0.85000 | Negative | Not ( P > 0.05) | |||||||||
406-168 | clay % | -1.98000 | Negative | moderately ( P < 0.05) | |||||||||
406-169 | 406 | Hoecker | 2,022 | Larch | Structural | Stem Density | Generalized Linear Models | 0.33 | pre-fire ba | 1.15000 | Positive | very high (P < 0.001) | Growing season maximum temperature |
406-169 | distance to low severity | -1.11000 | Negative | Not ( P > 0.05) | |||||||||
406-169 | post-fire vpd | 0.15000 | Positive | Not ( P > 0.05) | |||||||||
406-169 | aspect | 0.32000 | Negative | Not ( P > 0.05) | |||||||||
406-169 | soil organic material | -0.56000 | Negative | Not ( P > 0.05) | |||||||||
406-169 | clay % | 0.06000 | Positive | moderately ( P < 0.05) | |||||||||
406-170 | 406 | Hoecker | 2,022 | Douglas-Fir | Structural | Stem Density | Generalized Linear Models | 0.27 | pre-fire ba | 0.51000 | Positive | Not ( P > 0.05) | Growing season maximum temperature |
406-170 | distance to low severity | -3.83000 | Negative | very high (P < 0.001) | |||||||||
406-170 | post-fire vpd | 0.19000 | Positive | Not ( P > 0.05) | |||||||||
406-170 | aspect | -1.37000 | Negative | moderately ( P < 0.05) | |||||||||
406-170 | soil organic material | -1.17000 | Negative | Not ( P > 0.05) | |||||||||
406-170 | clay % | 1.67000 | Positive | Not ( P > 0.05) | |||||||||
117-151 | 117 | Kiel | 2,022 | Mixed Conifer | Spectral | Stem Density | Generalized Linear Models | 0.92 | distance to edge | -0.56000 | Negative | moderately ( P < 0.05) | slope, TPI |
117-151 | elevation | -0.26000 | Negative | moderately ( P < 0.05) | |||||||||
4058-157 | 4058 | Kiel | 2,025 | Mixed Conifer | Structural | Stem Density, biomass | Generalized linear model | 0.37 | intercept | 0.61300 | Positive | Conditional | |
4058-157 | elevation (m) | 0.20200 | Positive | Conditional | |||||||||
4058-157 | slope (percent) | 0.13000 | Positive | Conditional | |||||||||
4058-157 | tmi | -0.05800 | Positive | Conditional | |||||||||
4058-157 | soil clay content (percent) | 0.30200 | Positive | high (P <0.01) | |||||||||
4058-157 | winter snow water equivalent (30-year avg) | 0.17900 | Positive | Conditional | |||||||||
4058-157 | normal cmd | 0.20700 | Positive | Conditional | |||||||||
4058-157 | normal cmd | 0.20700 | Positive | Conditional | |||||||||
4058-157 | abundance of cone-bearing trees | Negative | very high (P < 0.001) | ||||||||||
4058-157 | seed source slope (categorical) | 0.22600 | Positive | moderately ( P < 0.05) | |||||||||
4058-157 | local seed source abundance | -0.10500 | Positive | Conditional | |||||||||
4058-157 | seed source direction | -0.10900 | Positive | Conditional | |||||||||
4058-177 | 4058 | Kiel | 2,025 | Mixed Conifer | Structural | Stem Density, biomass | Generalized linear model | 0.37 | elevation (m) | -0.29700 | Negative | high (P <0.01) | |
4058-177 | slope (percent) | 0.12100 | Positive | Not ( P > 0.05) | |||||||||
4058-177 | tmi | -0.19200 | Negative | Not ( P > 0.05) | |||||||||
4058-177 | soil clay content (percent) | -0.01500 | Negative | high (P <0.01) | |||||||||
4058-177 | winter snow water equivalent (30-year avg) | 0.47900 | Positive | very high (P < 0.001) | |||||||||
4058-177 | normal cmd | 0.18400 | Positive | Not ( P > 0.05) | |||||||||
4058-177 | normal cmd | 0.18400 | Positive | Not ( P > 0.05) | |||||||||
4058-177 | seed source slope (categorical) | 0.47000 | Positive | very high (P < 0.001) | |||||||||
4058-177 | local seed source abundance | -0.46900 | Negative | very high (P < 0.001) | |||||||||
4058-177 | seed source direction | -0.13400 | Negative | Not ( P > 0.05) | |||||||||
4058-178 | 4058 | Kiel | 2,025 | Mixed Conifer | Structural | Stem Density, biomass | Generalized linear model | 0.37 | elevation (m) | 0.50800 | Positive | very high (P < 0.001) | |
4058-178 | slope (percent) | 0.49600 | Positive | high (P <0.01) | |||||||||
4058-178 | tmi | 0.04400 | Positive | Not ( P > 0.05) | |||||||||
4058-178 | soil clay content (percent) | 0.33100 | Positive | very high (P < 0.001) | |||||||||
4058-178 | winter snow water equivalent (30-year avg) | 0.19800 | Positive | Not ( P > 0.05) | |||||||||
4058-178 | normal cmd | 0.31500 | Positive | very high (P < 0.001) | |||||||||
4058-178 | normal cmd | 0.31500 | Positive | very high (P < 0.001) | |||||||||
4058-178 | seed source slope (categorical) | 0.20100 | Positive | very high (P < 0.001) | |||||||||
4058-178 | local seed source abundance | -0.31400 | Positive | Not ( P > 0.05) | |||||||||
4058-178 | seed source direction | -0.49000 | Positive | Not ( P > 0.05) | |||||||||
4058-179 | 4058 | Kiel | 2,025 | Mixed Conifer | Structural | Stem Density, biomass | Generalized linear model | 0.37 | elevation (m) | 0.59800 | Positive | very high (P < 0.001) | |
4058-179 | slope (percent) | 0.05400 | Positive | very high (P < 0.001) | |||||||||
4058-179 | tmi | 0.30700 | Positive | very high (P < 0.001) | |||||||||
4058-179 | soil clay content (percent) | 0.62100 | Positive | very high (P < 0.001) | |||||||||
4058-179 | winter snow water equivalent (30-year avg) | -0.04500 | Negative | very high (P < 0.001) | |||||||||
4058-179 | normal cmd | 0.53700 | Positive | very high (P < 0.001) | |||||||||
4058-179 | normal cmd | 0.53700 | Positive | very high (P < 0.001) | |||||||||
4058-179 | seed source slope (categorical) | 0.27600 | Positive | very high (P < 0.001) | |||||||||
4058-179 | local seed source abundance | -0.18500 | Positive | Not ( P > 0.05) | |||||||||
4058-179 | seed source direction | -0.18500 | Positive | Not ( P > 0.05) | |||||||||
22-117 | 22 | Littlefield | 2,019 | Western Larch | Structural | Seedling / Sapling Precense | Logistic Regression | 0.54 | elevation | 0.01000 | Positive | moderately ( P < 0.05) | Slope, HLI, TPI, TWI, Extant cones on snags |
22-117 | shrub cover | 0.05200 | Positive | Not ( P > 0.05) | |||||||||
22-117 | distance to seed source | -0.99900 | Negative | high (P <0.01) | |||||||||
22-118 | 22 | Littlefield | 2,019 | Engelman Spruce | Structural | Seedling / Sapling Precense | Logistic Regression | 0.34 | elevation | 0.00600 | Positive | high (P <0.01) | HLI, TWI, Shrub cover (%), Extant cones on snags |
22-118 | slope | 0.11800 | Positive | Not ( P > 0.05) | |||||||||
22-118 | tpi | -0.02600 | Negative | moderately ( P < 0.05) | |||||||||
22-118 | tpi | -0.02600 | Negative | moderately ( P < 0.05) | |||||||||
22-118 | distance to seed source | 0.41700 | Positive | Not ( P > 0.05) | |||||||||
22-119 | 22 | Littlefield | 2,019 | ponderosa pine | Structural | Seedling / Sapling Precense | Logistic Regression | 0.4 | elevation | -0.00500 | Negative | moderately ( P < 0.05) | HLI, TWI, Shrub cover (%), Extant cones on snags |
22-119 | slope | -0.17600 | Negative | moderately ( P < 0.05) | |||||||||
22-119 | tpi | 0.02000 | Positive | moderately ( P < 0.05) | |||||||||
22-119 | tpi | 0.02000 | Positive | moderately ( P < 0.05) | |||||||||
22-119 | distance to seed source | 0.21200 | Positive | Not ( P > 0.05) | |||||||||
22-120 | 22 | Littlefield | 2,019 | Douglas fir | Structural | Seedling / Sapling Precense | Logistic Regression | 0.27 | shrub cover (%) | 0.04600 | Positive | moderately ( P < 0.05) | Elevation, slope, HLI, TPI, TWI, Extant cones on snags |
22-120 | distance to seed source | -0.56600 | Negative | high (P <0.01) | |||||||||
22-20 | 22 | Littlefield | 2,019 | Mixed Conifer | Structural | Stem Density | Generalized Linear Models | 0.24 | slope | -0.23400 | Negative | Not ( P > 0.05) | elevation, heat load index, topographic position index, topographic wetness index, extant cones on snags |
22-20 | shrub cover | -0.42100 | Negative | very high (P < 0.001) | |||||||||
22-20 | distance to edge | -0.39900 | Negative | high (P <0.01) | |||||||||
22-112 | 22 | Littlefield | 2,019 | Western Larch | Structural | Stem Density | Generalized Linear Models | 0.79 | elevation | 2.15900 | Positive | moderately ( P < 0.05) | Slope, HLI, TPI, TWI, Shrub Cover (%), Extant cones on snags |
22-112 | distance to edge | -2.15200 | Negative | very high (P < 0.001) | |||||||||
22-113 | 22 | Littlefield | 2,019 | Lodgepole pine | Structural | Stem Density | Generalized Linear Models | 0.3 | elevation | 0.55500 | Positive | moderately ( P < 0.05) | Slope, TWI |
22-113 | heat load index | -0.47900 | Negative | moderately ( P < 0.05) | |||||||||
22-113 | topographic position index | -0.61000 | Negative | moderately ( P < 0.05) | |||||||||
22-113 | shrub cover % | -0.42700 | Negative | moderately ( P < 0.05) | |||||||||
22-113 | distance to seed source | 0.32820 | Positive | moderately ( P < 0.05) | |||||||||
22-113 | extant cones on snags | -1.13200 | Negative | moderately ( P < 0.05) | |||||||||
22-114 | 22 | Littlefield | 2,019 | Engelman Spruce | Structural | Stem Density | Generalized Linear Models | 0.5 | elevation | 1.44200 | Positive | high (P <0.01) | HLI, TWI, Shrub cover(%), extant cones on snags |
22-114 | slope | 0.90700 | Positive | Not ( P > 0.05) | |||||||||
22-114 | tpi | -1.65500 | Negative | moderately ( P < 0.05) | |||||||||
22-114 | tpi | -1.65500 | Negative | moderately ( P < 0.05) | |||||||||
22-114 | distance to seed source | -0.59600 | Negative | Not ( P > 0.05) | |||||||||
22-115 | 22 | Littlefield | 2,019 | Ponderosa Pine | Structural | Stem Density | Generalized Linear Models | 0.58 | elevation | -2.60300 | Negative | very high (P < 0.001) | HLI, TWI, Shrub cover (%), Extant cones on snags |
22-115 | tpi | -0.68000 | Negative | moderately ( P < 0.05) | |||||||||
22-115 | tpi | -0.68000 | Negative | moderately ( P < 0.05) | |||||||||
22-115 | twi | 1.15700 | Positive | high (P <0.01) | |||||||||
22-116 | 22 | Littlefield | 2,019 | Douglas-fir | Structural | Stem Density | Generalized Linear Models | 0.46 | elevation | -0.45700 | Negative | moderately ( P < 0.05) | HLI, TWI, Shrub cover (%), Extant cones on snags |
22-116 | slope | 0.43300 | Positive | moderately ( P < 0.05) | |||||||||
22-116 | twi | -0.29200 | Negative | Not ( P > 0.05) | |||||||||
22-116 | distance to seed source | -1.07000 | Negative | very high (P < 0.001) | |||||||||
215-46 | 215 | Malone | 2,018 | Mixed Conifer | Structural | Stem Density | spatial pattern density models | na | distance to edge | -0.03600 | Negative | high (P <0.01) | |
215-46 | severity | 0.84200 | Positive | very high (P < 0.001) | |||||||||
215-46 | twi | -0.00700 | Negative | very high (P < 0.001) | |||||||||
215-46 | distance to aspen | -0.00700 | Negative | very high (P < 0.001) | |||||||||
215-46 | elevation | -0.11200 | Negative | very high (P < 0.001) | |||||||||
215-75 | 215 | Malone | 2,018 | Mixed Conifer | Structural | Stem Density | spatial pattern density models | distance to edge | -0.04200 | Negative | high (P <0.01) | elevation, TWI, distance to aspen | |
215-75 | severity | 0.93900 | Positive | very high (P < 0.001) | |||||||||
215-76 | 215 | Malone | 2,018 | Mixed Conifer | Structural | Stem Density | spatial pattern density models | severity | 0.30100 | Positive | very high (P < 0.001) | ||
215-76 | elevation | 0.00180 | Negative | very high (P < 0.001) | |||||||||
215-76 | distance to aspen | 0.00200 | Positive | very high (P < 0.001) | |||||||||
215-76 | twi | 0.00200 | Positive | very high (P < 0.001) | |||||||||
249-47 | 249 | McKenzie | 2,012 | Mixed Conifer | Structural | Stem Density, Composition | Canonical Correspondence Analysis | elevation | Positive | slope, aspect, soil texture, pH, Soil Nitrogen | |||
249-47 | time since fire | Positive | |||||||||||
1-13 | 1 | Menick | 2,024 | Mixed Conifer | Spectral | Seedling / Sapling Precense | Random Forests | 0.98 | douglas-fir pre-fire | 1.99900 | Positive | very high (P < 0.001) | |
1-13 | lodgepole pre-fire | 6.00000 | Positive | very high (P < 0.001) | |||||||||
1-13 | lodgepole vs. douglas fir | 3.00200 | Positive | very high (P < 0.001) | |||||||||
1-13 | normal cwd | 0.95800 | Negative | very high (P < 0.001) | |||||||||
1-13 | patch size | 0.99000 | Negative | moderately ( P < 0.05) | |||||||||
1-13 | patch size | 0.99000 | Negative | moderately ( P < 0.05) | |||||||||
1-13 | patch size | 0.99000 | Negative | moderately ( P < 0.05) | |||||||||
1-13 | patch area to perimeter ratio | 0.99200 | Negative | very high (P < 0.001) | |||||||||
1-13 | elevation | 0.99700 | Negative | very high (P < 0.001) | |||||||||
1-13 | slope | 0.89900 | Negative | very high (P < 0.001) | |||||||||
1-13 | aspect | 1.63500 | Negative | very high (P < 0.001) | |||||||||
196-45 | 196 | Mitchell | 2,010 | Ponderosa Pine | Spectral | Composition | Generalized Linear Models | 0.171 | dnbr | 0.03174 | Positive | very high (P < 0.001) | |
196-45 | aspect | -0.00600 | Negative | very high (P < 0.001) | |||||||||
196-45 | elevation | 0.00370 | Positive | very high (P < 0.001) | |||||||||
196-45 | soil erodibility | 0.10400 | Positive | ||||||||||
234-142 | 234 | Peeler | 2,020 | Subalpine Fir | Structural | Seedling / Sapling Precense | Logistic Regression | 0.34 | distance to seed source | -0.06300 | Negative | moderately ( P < 0.05) | FireID (time since fire & climate), openness of terrain in 50m radius, percentage of landscape measured at 25/50/100/150/200/250m radii, fractal dimension measured at 25/50/100/150/200/250m radii, contagion measured at 25/50/100/150/200/250m radii |
234-144 | 234 | Peeler | 2,020 | Lodgepole Pine | Structural | Seedling / Sapling Precense | Logistic Regression | 0.237 | distance to seed source | -0.00300 | Negative | moderately ( P < 0.05) | FireID (time since fire & climate), openness of terrain in 50m radius, percentage of landscape measured at 25/50/100/150/200/250m radii, fractal dimension measured at 25/50/100/150/200/250m radii, contagion measured at 25/50/100/150/200/250m radii |
234-143 | 234 | Peeler | 2,020 | Subalpine Fir | Structural | Stem Density | Logistic Regression | 0.235 | percentage of landscape covered by seed source at 100m radius | -0.02100 | Negative | moderately ( P < 0.05) | distance to seed source, FireID (time since fire & climate), openness of terrain in 100m radius, percentage of landscape measured at 25/50/150/200/250m radii, fractal dimension measured at 25/50/100/150/200/250m radii, contagion measured at 25/50/100/150/200/250m radii |
234-145 | 234 | Peeler | 2,020 | Lodgepole Pine | Structural | Stem Density | Logistic Regression | 0.365 | percentage of landscape covered by seed source at 25m radius | 0.03300 | Positive | moderately ( P < 0.05) | distance to seed source, FireID (time since fire & climate), percentage of landscape measured at 50/100/150/200/250m radii, fractal dimension measured at 25/50/100/150/200/250m radii, contagion measured at 50/100/150/200/250m radii |
234-145 | contagion (landscape metric) at 25m radius | 0.01500 | Positive | moderately ( P < 0.05) | |||||||||
234-145 | openness at 200m radius | 0.02000 | Positive | moderately ( P < 0.05) | |||||||||
53-26 | 53 | Peven | 2,024 | Pinus contorta | Structural | Stem Density | Generalized Linear Models | 0.369 | distance to spring | -0.30970 | Negative | high (P <0.01) | distance to edge, slope, heat load index, post-fire growing season precipitation (5-year avg.), post-fire maximum seasonal precipitation (5-year avg) |
53-26 | elevation | 0.80430 | Positive | very high (P < 0.001) | |||||||||
53-27 | 53 | Peven | 2,024 | Douglas Fir | Structural | Stem Density | Generalized Linear Models | 0.346 | distance to spring | -0.30000 | Negative | high (P <0.01) | distance to edge, slope, heat load index, post-fire growing season precipitation (5-year avg.), post-fire maximum seasonal precipitation (5-year avg) |
53-27 | heat load index | -0.35000 | Negative | Not ( P > 0.05) | |||||||||
53-27 | distance to edge | -0.76000 | Negative | very high (P < 0.001) | |||||||||
53-27 | slope | -0.20000 | Negative | Not ( P > 0.05) | |||||||||
53-101 | 53 | Peven | 2,024 | Lodgepole pine | Structural | Stem Density | Generalized Linear Models | 0.384 | distance to spring | -0.31550 | Negative | high (P <0.01) | distance to edge, slope, heat load index, post-fire growing season precipitation (5-year avg.), post-fire maximum seasonal precipitation (5-year avg) |
53-101 | slope | -0.47690 | Negative | moderately ( P < 0.05) | |||||||||
53-101 | heat load index | 0.54840 | Positive | high (P <0.01) | |||||||||
17-19 | 17 | Povak | 2,020 | Mixed conifer | Structural | Stem Density | Generalized Additive Models | Not reported | normal mat | Negative | high (P <0.01) | ||
17-19 | normal map | Positive | Not ( P > 0.05) | ||||||||||
17-19 | anomalous mean mat | Positive | Conditional | ||||||||||
17-19 | anomalous mean map | Positive | very high (P < 0.001) | ||||||||||
17-19 | aspect | Negative | moderately ( P < 0.05) | ||||||||||
17-19 | post-fire basal area | Positive | Conditional | ||||||||||
17-19 | post-fire overstory quadratic mean diameter | Positive | Conditional | ||||||||||
17-19 | grass % | Negative | very high (P < 0.001) | ||||||||||
17-19 | distance to edge | Negative | very high (P < 0.001) | ||||||||||
17-107 | 17 | Povak | 2,020 | Douglas Fir | Structural | Stem Density | Generalized Additive Models | Not reported | normal mat | Positive | high (P <0.01) | ||
17-107 | normal map | Positive | moderately ( P < 0.05) | ||||||||||
17-107 | anomalous mean mat | Positive | Conditional | ||||||||||
17-107 | anomalous mean map | Positive | very high (P < 0.001) | ||||||||||
17-107 | aspect | Negative | Not ( P > 0.05) | ||||||||||
17-107 | post-fire basal area | Positive | high (P <0.01) | ||||||||||
17-107 | post-fire overstory quadratic mean diameter | Negative | very high (P < 0.001) | ||||||||||
17-107 | grass % | Negative | very high (P < 0.001) | ||||||||||
17-107 | distance to edge | Negative | very high (P < 0.001) | ||||||||||
17-108 | 17 | Povak | 2,020 | Ponderosa Pine | Structural | Stem Density | Generalized Additive Models | Not reported | normal mat | Negative | Not ( P > 0.05) | ||
17-108 | normal map | Positive | Not ( P > 0.05) | ||||||||||
17-108 | anomalous mean mat | Positive | Not ( P > 0.05) | ||||||||||
17-108 | anomalous mean map | Positive | Not ( P > 0.05) | ||||||||||
17-108 | aspect | Negative | moderately ( P < 0.05) | ||||||||||
17-108 | post-fire basal area | Positive | high (P <0.01) | ||||||||||
17-108 | post-fire overstory quadratic mean diameter | Positive | high (P <0.01) | ||||||||||
17-108 | grass % | Positive | high (P <0.01) | ||||||||||
17-108 | distance to edge | Negative | very high (P < 0.001) | ||||||||||
17-109 | 17 | Povak | 2,020 | Lodgepole pine | Structural | Stem Density | Generalized Additive Models | Not reported | normal mat | Negative | high (P <0.01) | ||
17-109 | normal map | Positive | moderately ( P < 0.05) | ||||||||||
17-109 | anomalous mean mat | Positive | very high (P < 0.001) | ||||||||||
17-109 | anomalous mean map | Positive | Not ( P > 0.05) | ||||||||||
17-109 | aspect | Positive | Not ( P > 0.05) | ||||||||||
17-109 | post-fire basal area | Positive | high (P <0.01) | ||||||||||
17-109 | post-fire overstory quadratic mean diameter | Positive | high (P <0.01) | ||||||||||
17-109 | grass % | Negative | very high (P < 0.001) | ||||||||||
17-109 | distance to edge | Negative | very high (P < 0.001) | ||||||||||
17-110 | 17 | Povak | 2,020 | Western Larch | Structural | Stem Density | Generalized Additive Models | Not reported | normal mat | Negative | moderately ( P < 0.05) | ||
17-110 | normal map | Positive | Not ( P > 0.05) | ||||||||||
17-110 | anomalous mean mat | Positive | very high (P < 0.001) | ||||||||||
17-110 | anomalous mean map | Positive | Not ( P > 0.05) | ||||||||||
17-110 | aspect | Negative | very high (P < 0.001) | ||||||||||
17-110 | post-fire basal area | Positive | very high (P < 0.001) | ||||||||||
17-110 | post-fire overstory quadratic mean diameter | Positive | high (P <0.01) | ||||||||||
17-110 | grass % | Negative | high (P <0.01) | ||||||||||
17-110 | distance to edge | Negative | high (P <0.01) | ||||||||||
17-111 | 17 | Povak | 2,020 | Engelman Spruce | Structural | Stem Density | Generalized Additive Models | Not reported | normal mat | Positive | high (P <0.01) | ||
17-111 | normal map | Positive | moderately ( P < 0.05) | ||||||||||
17-111 | anomalous mean mat | Positive | moderately ( P < 0.05) | ||||||||||
17-111 | anomalous mean map | Positive | Not ( P > 0.05) | ||||||||||
17-111 | aspect | Negative | very high (P < 0.001) | ||||||||||
17-111 | post-fire basal area | Positive | Not ( P > 0.05) | ||||||||||
17-111 | post-fire overstory quadratic mean diameter | Positive | high (P <0.01) | ||||||||||
17-111 | grass % | Negative | high (P <0.01) | ||||||||||
17-111 | distance to edge | Positive | high (P <0.01) | ||||||||||
47-24 | 47 | Rodman | 2,020 | Douglas Fir | Structural | Stem Density | Generalized Linear Models | 0.804 | distance to edge squared | -0.18710 | Negative | very high (P < 0.001) | RdNBR, Time since Fire, Clay content (%), soil ph, Average Actual Evapotranspiration, Average CWD, Anomalous Post-fire Average Actual Evapotranspiration, Anomalous POst-fire Growing season precipitation |
47-24 | normal cmd | -0.00750 | Negative | high (P <0.01) | |||||||||
47-24 | normal cmd | -0.00750 | Negative | high (P <0.01) | |||||||||
47-24 | tpi | -0.10350 | Negative | Not ( P > 0.05) | |||||||||
47-24 | tpi | -0.10350 | Negative | Not ( P > 0.05) | |||||||||
47-24 | hli | -3.86450 | Negative | very high (P < 0.001) | |||||||||
47-24 | anomalous maximum cmd | -0.87310 | Negative | Not ( P > 0.05) | |||||||||
47-24 | normal growing season precipitation | 0.01390 | Positive | Not ( P > 0.05) | |||||||||
47-24 | tpi : normal precipitation | 0.00020 | Positive | Not ( P > 0.05) | |||||||||
47-106 | 47 | Rodman | 2,020 | Ponderosa Pine | Structural | Stem Density | Generalized Linear Models | 0.804 | distance to edge squared | -0.09800 | Negative | very high (P < 0.001) | Heat Load Index, RdNBR, Time since Fire, Clay content (%), soil ph, Average Actual Evapotranspiration, Average CWD, Anomalous Post-fire Average Actual Evapotranspiration, Anomalous POst-fire Growing season precipitation |
47-106 | growing season precipitation | 0.00970 | Negative | high (P <0.01) | |||||||||
47-106 | tpi | -0.06440 | Negative | Not ( P > 0.05) | |||||||||
47-106 | tpi | -0.06440 | Negative | Not ( P > 0.05) | |||||||||
47-106 | normal cmd | -0.00340 | Negative | very high (P < 0.001) | |||||||||
47-106 | normal cmd | -0.00340 | Negative | very high (P < 0.001) | |||||||||
47-106 | anomalous maximum cmd | -1.07540 | Negative | Not ( P > 0.05) | |||||||||
47-106 | tpi : precipitation | 0.00020 | Positive | Not ( P > 0.05) | |||||||||
283-48 | 283 | Schapira | 2,021 | Subalpine Fir | Structural | Seedling Establishment | NMDS | anomalous growing season minimum temperature | Negative | high (P <0.01) | |||
283-48 | anomalous growing season precipitation | Positive | very high (P < 0.001) | ||||||||||
283-48 | anomalous annual vpd | Negative | moderately ( P < 0.05) | ||||||||||
283-48 | anomalous cwd | Negative | very high (P < 0.001) | ||||||||||
283-121 | 283 | Schapira | 2,021 | Engelman Spruce | Structural | Seedling Establishment | Groups years with large to small establishment and compares to differences in climate | Not applicable | anomalous growing season minimum temperature | Negative | high (P <0.01) | ||
283-121 | anomalous growing season precipitation | Positive | very high (P < 0.001) | ||||||||||
283-121 | anomalous annual vpd | Negative | moderately ( P < 0.05) | ||||||||||
283-121 | anomalous cwd | Negative | very high (P < 0.001) | ||||||||||
57-28 | 57 | Shrestha | 2,024 | Mixed Conifer | Spectral | Random Forest | 0.73 | dnbr | 0.02420 | Positive | moderately ( P < 0.05) | ||
57-28 | normal precipitation | 0.06120 | Positive | moderately ( P < 0.05) | |||||||||
57-28 | normal precipitation | 0.06120 | Positive | moderately ( P < 0.05) | |||||||||
57-28 | normal annual temperature | 0.06200 | Positive | moderately ( P < 0.05) | |||||||||
57-28 | elevation | 0.08610 | Negative | moderately ( P < 0.05) | |||||||||
57-77 | 57 | Shrestha | 2,024 | Lodgepole pine | Spectral | Random Forests | 0.73 | dnbr | 0.02380 | Negative | moderately ( P < 0.05) | ||
57-77 | normal precipitation | 0.02970 | Positive | moderately ( P < 0.05) | |||||||||
57-77 | normal precipitation | 0.02970 | Positive | moderately ( P < 0.05) | |||||||||
57-77 | normal annual temperature | 0.02030 | Positive | moderately ( P < 0.05) | |||||||||
57-77 | elevation | 0.05800 | Negative | moderately ( P < 0.05) | |||||||||
57-78 | 57 | Shrestha | 2,024 | Douglas Fir | Spectral | Random Forests | 0.65 | dnbr | 0.01800 | Negative | moderately ( P < 0.05) | ||
57-78 | normal precipitation | 0.08200 | Positive | moderately ( P < 0.05) | |||||||||
57-78 | normal precipitation | 0.08200 | Positive | moderately ( P < 0.05) | |||||||||
57-78 | normal annual temperature | 0.10000 | Positive | moderately ( P < 0.05) | |||||||||
57-78 | elevation | 0.18000 | Negative | moderately ( P < 0.05) | |||||||||
57-79 | 57 | Shrestha | 2,024 | Ponderosa Pine | Spectral | Random Forests | 0.78 | dnbr | 0.01000 | Negative | moderately ( P < 0.05) | ||
57-79 | normal precipitation | 0.12000 | Positive | moderately ( P < 0.05) | |||||||||
57-79 | normal precipitation | 0.12000 | Positive | moderately ( P < 0.05) | |||||||||
57-79 | normal annual temperature | 0.13000 | Negative | moderately ( P < 0.05) | |||||||||
57-79 | elevation | 0.20000 | Positive | moderately ( P < 0.05) | |||||||||
57-80 | 57 | Shrestha | 2,024 | Pinyon Juniper | Spectral | Random Forests | 0.7 | dnbr | 0.01600 | Positive | moderately ( P < 0.05) | ||
57-80 | normal precipitation | 0.09900 | Positive | moderately ( P < 0.05) | |||||||||
57-80 | normal precipitation | 0.09900 | Positive | moderately ( P < 0.05) | |||||||||
57-80 | normal annual temperature | 0.12100 | Positive | moderately ( P < 0.05) | |||||||||
57-80 | elevation | 0.15500 | Positive | moderately ( P < 0.05) | |||||||||
57-81 | 57 | Shrestha | 2,024 | Oak | Spectral | Random Forests | 0.66 | dnbr | 0.07000 | Positive | moderately ( P < 0.05) | ||
57-81 | normal precipitation | 0.21000 | Positive | moderately ( P < 0.05) | |||||||||
57-81 | normal precipitation | 0.21000 | Positive | moderately ( P < 0.05) | |||||||||
57-81 | normal annual temperature | 0.27000 | Negative | moderately ( P < 0.05) | |||||||||
57-81 | elevation | 0.36000 | Negative | moderately ( P < 0.05) | |||||||||
57-82 | 57 | Shrestha | 2,024 | Spruce/Fir/Hemlock | Spectral | Random Forests | 0.77 | dnbr | 0.03200 | Negative | moderately ( P < 0.05) | ||
57-82 | normal precipitation | 0.02500 | Positive | moderately ( P < 0.05) | |||||||||
57-82 | normal precipitation | 0.02500 | Positive | moderately ( P < 0.05) | |||||||||
57-82 | normal annual temperature | 0.03600 | Positive | moderately ( P < 0.05) | |||||||||
57-82 | elevation | 0.11000 | Negative | moderately ( P < 0.05) | |||||||||
1508-132 | 1508 | Stevens-Rumann | 2,016 | Mixed Conifer | Structural | Basal area | distance to seed source | 10.67000 | Negative | very high (P < 0.001) | aspect | ||
1508-132 | slope | 3.29735 | Negative | very high (P < 0.001) | |||||||||
1508-132 | aspect | 0.79918 | Positive | very high (P < 0.001) | |||||||||
3955-148 | 3955 | Stevens-Rumann | 2,018 | Mixed Conifer | Structural | Seedling / Sapling Precense | Generalized Linear Models | 0.91 | normal cmd | 0.01800 | Positive | high (P <0.01) | |
3955-148 | normal cmd | 0.01800 | Positive | high (P <0.01) | |||||||||
3955-148 | anomalous cmd | -15.64000 | Negative | very high (P < 0.001) | |||||||||
3955-148 | canopy mortality (binary) | -0.43400 | Negative | Not ( P > 0.05) | |||||||||
3955-148 | hli | 15.54000 | Positive | high (P <0.01) | |||||||||
3955-148 | distance to seed source | -0.00700 | Negative | high (P <0.01) | |||||||||
3955-148 | anomalous cmd : normal cmd | 0.02900 | Positive | high (P <0.01) | |||||||||
3955-171 | 3955 | Stevens-Rumann | 2,018 | Mixed Conifer | Structural | Seedling / Sapling Precense | Generalized Linear Models | 0.86 | normal cmd | -0.00400 | Positive | very high (P < 0.001) | |
3955-171 | normal cmd | -0.00400 | Positive | very high (P < 0.001) | |||||||||
3955-171 | anomalous cmd | -2.02400 | Negative | Not ( P > 0.05) | |||||||||
3955-171 | canopy mortality (binary) | -0.12000 | Negative | Not ( P > 0.05) | |||||||||
3955-171 | hli | 1.07400 | Positive | Not ( P > 0.05) | |||||||||
3955-171 | distance to seed source | -0.00100 | Negative | high (P <0.01) | |||||||||
3955-171 | anomalous cmd : normal cmd | 0.00300 | Positive | Not ( P > 0.05) | |||||||||
3004-64 | 3004 | Talucci | 2,019 | Mixed Conifer | Structural | Stem Density | Generalized Linear Models | prefire beetle mortality | 2.59000 | Positive | Not ( P > 0.05) | ||
3004-64 | extant cones | -0.98000 | Negative | moderately ( P < 0.05) | |||||||||
3004-64 | branches on remaining trees | 0.14600 | Positive | Not ( P > 0.05) | |||||||||
3004-64 | bare soil | 0.27000 | Positive | Not ( P > 0.05) | |||||||||
3004-64 | post-fire frost free days | 0.99000 | Positive | Not ( P > 0.05) | |||||||||
3004-64 | post-fire snow accumulation | 0.93000 | Positive | high (P <0.01) | |||||||||
3004-64 | cmd | 0.99000 | Positive | Not ( P > 0.05) | |||||||||
1395-149 | 1395 | Turner | 2,019 | Mixed Conifer | Structural | Stem Density | ANOVA | 0.62 | cones on lodgepole trees | -0.62000 | Negative | very high (P < 0.001) | Bole score, Char %, pre-fire stand density, distance to edge. |
188-9 | 188 | Turner | 2,016 | Mixed Conifer | Structural | Aboveground net primary production | Generalized Linear Models | 0.78 | lodgepole pine density | 0.26000 | Positive | ||
188-9 | soil substrate class | -0.11000 | Negative | ||||||||||
188-9 | distance to edge | -0.00050 | Negative | ||||||||||
188-9 | post-fire mean annual precipitation | -0.00020 | Negative | ||||||||||
1916-61 | 1916 | Turner | 2,004 | Lodgepole Pine | Structural | Stem Density | Correlation | 0.37 | elevation | 43.13600 | Negative | very high (P < 0.001) | soil type, fire severity |
1916-61 | distance to edge | 3.92200 | Positive | moderately ( P < 0.05) | |||||||||
243-172 | 243 | Turner | 1,997 | Mixed Conifer | Structural | Composition | ANOVA | Not provided | site | 130.28000 | Positive | very high (P < 0.001) | |
243-172 | patch size | Positive | Not ( P > 0.05) | ||||||||||
243-172 | patch size | Positive | Not ( P > 0.05) | ||||||||||
243-172 | patch size | Positive | Not ( P > 0.05) | ||||||||||
243-172 | burn severity | 6.75000 | Positive | very high (P < 0.001) | |||||||||
243-172 | burn severity | 6.75000 | Positive | very high (P < 0.001) | |||||||||
243-172 | burn severity | 6.75000 | Positive | very high (P < 0.001) | |||||||||
243-172 | slope | Positive | Not ( P > 0.05) | ||||||||||
243-172 | location : patch size | 5.35000 | Positive | very high (P < 0.001) | |||||||||
243-172 | location : burn severity | 7.24000 | Positive | very high (P < 0.001) | |||||||||
243-172 | patch size :burn severity | Positive | Not ( P > 0.05) | ||||||||||
243-172 | location:patch:burnseverity | Positive | Not ( P > 0.05) | ||||||||||
243-172 | aspect | Positive | Not ( P > 0.05) | ||||||||||
243-172 | distance to edge | Positive | Not ( P > 0.05) | ||||||||||
243-172 | distance to severe burn | Positive | |||||||||||
243-150 | 243 | Turner | 1,997 | Mixed Conifer | Structural | Stem Density | ANOVA | 0.64 | site | 15.80000 | Positive | very high (P < 0.001) | |
243-150 | patch size | 3.70000 | Positive | high (P <0.01) | |||||||||
243-150 | patch size | 3.70000 | Positive | high (P <0.01) | |||||||||
243-150 | patch size | 3.70000 | Positive | high (P <0.01) | |||||||||
243-150 | burn severity | 12.42000 | Positive | very high (P < 0.001) | |||||||||
243-150 | burn severity | 12.42000 | Positive | very high (P < 0.001) | |||||||||
243-150 | burn severity | 12.42000 | Positive | very high (P < 0.001) | |||||||||
243-150 | serotiny | 69.12000 | Positive | very high (P < 0.001) | |||||||||
243-150 | location : patch size | 10.22000 | Positive | very high (P < 0.001) | |||||||||
243-150 | location : burn severity | 10.22000 | Positive | very high (P < 0.001) | |||||||||
243-150 | patch size :burn severity | Positive | Not ( P > 0.05) | ||||||||||
243-150 | location:patch:burnseverity | 2.96000 | Positive | high (P <0.01) | |||||||||
49-102 | 49 | Urza | 2,017 | Lodgepole pine | Structural | Stem Density | Mixed Linear Models | Not reported | pre-fire abundance of lodgepole pine | 3.39000 | Positive | high (P <0.01) | extreme burn severity, high burn severity, moderate burn severity, heat load, distance to edge, distance to edge quadratic, heat load, elevation |
49-102 | random effect for age | 0.82000 | Negative | Not ( P > 0.05) | |||||||||
49-103 | 49 | Urza | 2,017 | Larch | Structural | Stem Density | Mixed Linear Models | Not reported | extreme burn severity | 3.13000 | Positive | moderately ( P < 0.05) | prefire abundance, elevation |
49-103 | high burn severity | 2.45000 | Positive | Not ( P > 0.05) | |||||||||
49-103 | moderate burn severity | 1.20000 | Positive | Not ( P > 0.05) | |||||||||
49-103 | distance to edge (quadratic) | 0.07000 | Negative | high (P <0.01) | |||||||||
49-103 | distance to edge | 0.29000 | Negative | moderately ( P < 0.05) | |||||||||
49-103 | random effect stand age | 1.19000 | Positive | Not ( P > 0.05) | |||||||||
49-103 | heat load | 1.24000 | Positive | Not ( P > 0.05) | |||||||||
49-104 | 49 | Urza | 2,017 | Englemann spruce/Subalpine fir | Structural | Stem Density | Mixed Linear Models | Not reported | pre-fire spruce abundance | 0.57000 | Positive | Not ( P > 0.05) | extreme burn severity, high burn severity, moderate burn severity, heat load |
49-104 | distance to edge quadratic | 0.14000 | Negative | moderately ( P < 0.05) | |||||||||
49-104 | distance to edge | 0.32000 | Negative | Not ( P > 0.05) | |||||||||
49-104 | random effect stand age | 2.58000 | Positive | high (P <0.01) | |||||||||
49-104 | elevation | 1.99000 | Positive | Not ( P > 0.05) | |||||||||
49-105 | 49 | Urza | 2,017 | Douglas Fir | Structural | Stem Density | Mixed Linear Models | Not reported | pre-fire douglas fir abundance | 1.67000 | Positive | moderately ( P < 0.05) | extreme burn severity, high burn severity, moderate burn severity, years since fire |
49-105 | distance to seed source quadratic | 0.19000 | Negative | high (P <0.01) | |||||||||
49-105 | distance to edge | 1.34000 | Positive | Not ( P > 0.05) | |||||||||
49-105 | heat load | 0.80000 | Negative | Not ( P > 0.05) | |||||||||
49-105 | elevation | 1.68000 | Positive | very high (P < 0.001) | |||||||||
49-25 | 49 | Urza | 2,017 | Mixed Conifer | Structural | Stem Density, Composition | Mixed Linear Models | Not reported | post-fire growing degree days | Positive | moderately ( P < 0.05) | ||
49-25 | distance to edge | Positive | moderately ( P < 0.05) | ||||||||||
49-25 | dnbr | Positive | moderately ( P < 0.05) | ||||||||||
49-25 | distance to live spruce | Positive | moderately ( P < 0.05) | ||||||||||
49-25 | post-fire winter precipitation | Negative | moderately ( P < 0.05) | ||||||||||
49-25 | post-fire growing season precipitation | Negative | moderately ( P < 0.05) | ||||||||||
49-25 | remaining douglas-fir post-fire | Negative | moderately ( P < 0.05) | ||||||||||
138-43 | 138 | Vanderhoof | 2,021 | Coniferous Forest (Growing Season) | Spectral | Composition | Random Forest | 0.725 | rdnbr | 123.50000 | Positive | very high (P < 0.001) | annual precipitation, summer precipitation, anomalous precipitation, anomalous winter precipitation, anomalous summer precipitation, maximum summer temperature, minimum summer temperature, minimum winter temperature, anomalous minimum summer temperature, anomalous minimum winter temperature, VPD, slope, aspect, distance-to-edge, elevation |
138-43 | pet | 12.10000 | Positive | high (P <0.01) | |||||||||
138-43 | growing degree days | 20.00000 | Negative | moderately ( P < 0.05) | |||||||||
138-43 | winter precipitation | 12.90000 | Positive | moderately ( P < 0.05) | |||||||||
138-43 | winter minimum temperature | 19.00000 | Positive | moderately ( P < 0.05) | |||||||||
138-43 | anomalous maximum summer temperature | 38.40000 | Negative | high (P <0.01) | |||||||||
138-43 | anomalous maximum summer vpd | 21.90000 | Negative | high (P <0.01) | |||||||||
138-42 | 138 | Vanderhoof | 2,021 | Coniferous (snow-cover model) | Spectral | Stem Density | Random Forests | 0.684 | summer precipitation | 16.00000 | Negative | high (P <0.01) | RdNBR, annual precipitation, winter precipitation, anomalous precipitation, anomalous winter precipitation, anomalous summer precipitation, maximum summer temperature, minimum summer temperature, minimum winter temperature, anomalous maximum summer temperature, anomalous minimum summer temperature, anomalous minimum winter temperature, VPD, anomalous VPD, slope, aspect, distance-to-edge |
138-42 | pet (anomaly) | 43.90000 | Positive | very high (P < 0.001) | |||||||||
138-42 | growing degree days | 22.50000 | Positive | high (P <0.01) | |||||||||
138-42 | summer maximum temp | 13.90000 | Positive | moderately ( P < 0.05) | |||||||||
138-42 | summer minimum temperatures | 31.00000 | Positive | very high (P < 0.001) | |||||||||
138-42 | winter minimum temperature | 15.30000 | Negative | moderately ( P < 0.05) | |||||||||
138-42 | elevation | 20.90000 | Negative | high (P <0.01) | |||||||||
144-30 | 144 | Wilson | 2,021 | Douglas Fir | Spectral | Boosted Regression Trees | 0.42 | anomalous snow-cover 1 year post-fire | 8.00000 | Negative | high (P <0.01) | ||
144-30 | anomalous snow-cover 3 years post-fire | 18.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-30 | anomalous precipitation | 26.00000 | Positive | high (P <0.01) | |||||||||
144-30 | elevation | 19.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-30 | slope | 6.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-30 | aspect | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-30 | pre-fire composition | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-30 | burn severity stdev | 5.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-30 | rdnbr | 5.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | 144 | Wilson | 2,021 | Sub Alpine Fir / Engelman Spruce | Spectral | Boosted Regression Trees | 0.69 | anomalous snow-cover 1 year post-fire | 3.00000 | Positive | high (P <0.01) | ||
144-83 | anomalous snow-cover 3 year mean | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | anomalous precipitation 1 year post fire | 34.00000 | Positive | high (P <0.01) | |||||||||
144-83 | anomalous precipitation 3 year mean | 3.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | elevation | 10.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | slope | 14.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | aspect (southness) | 2.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | pre-fire composition | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | burn severity stdev | 10.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-83 | rdnbr | 12.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-84 | 144 | Wilson | 2,021 | Grand fir | Spectral | Boosted Regression Trees | 0.7 | anomalous snow-cover 1 year post-fire | 19.00000 | Negative | moderately ( P < 0.05) | ||
144-84 | anomalous snow-cover 3 year mean | 16.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | anomalous precipitation 1 year post fire | 7.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | anomalous precipitation 3 year mean | 22.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | elevation | 6.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | slope | 16.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-84 | aspect (southness) | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | pre-fire composition | 7.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | burn severity stdev | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-84 | rdnbr | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-85 | 144 | Wilson | 2,021 | Mountain hemlock | Spectral | Boosted Regression Trees | 0.57 | anomalous snow-cover 1 year post-fire | 0.00000 | Positive | moderately ( P < 0.05) | ||
144-85 | anomalous snow-cover 3 year mean | 14.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-85 | anomalous precipitation 1 year post fire | 28.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-85 | anomalous precipitation 3 year mean | 24.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-85 | elevation | 12.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-85 | slope | 9.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-85 | aspect (southness) | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-85 | pre-fire composition | 5.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-85 | burn severity stdev | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-85 | rdnbr | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | 144 | Wilson | 2,021 | Douglas fir | Spectral | Boosted Regression Trees | 0.43 | anomalous snow-cover 1 year post-fire | 7.00000 | Positive | moderately ( P < 0.05) | ||
144-86 | anomalous snow-cover 3 year mean | 7.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | anomalous precipitation 1 year post fire | 12.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-86 | anomalous precipitation 3 year mean | 14.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | elevation | 37.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | slope | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | aspect (southness) | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | pre-fire composition | 10.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-86 | burn severity stdev | 5.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-86 | rdnbr | 8.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-87 | 144 | Wilson | 2,021 | Englemann spruce/Subalpine fir | Spectral | Boosted Regression Trees | 0.39 | anomalous snow-cover 1 year post-fire | 5.00000 | Positive | moderately ( P < 0.05) | ||
144-87 | anomalous snow-cover 3 year mean | 5.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-87 | anomalous precipitation 1 year post fire | 21.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-87 | anomalous precipitation 3 year mean | 40.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-87 | elevation | 18.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-87 | slope | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-87 | aspect (southness) | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-87 | pre-fire composition | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-87 | burn severity stdev | 2.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-87 | rdnbr | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | 144 | Wilson | 2,021 | Douglas fir | Spectral | Boosted Regression Trees | 0.33 | anomalous snow-cover 1 year post-fire | 0.00000 | Positive | moderately ( P < 0.05) | ||
144-88 | anomalous snow-cover 3 year mean | 3.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | anomalous precipitation 1 year post fire | 42.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | anomalous precipitation 3 year mean | 44.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | elevation | 10.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | slope | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | aspect (southness) | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | pre-fire composition | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | burn severity stdev | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-88 | rdnbr | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-89 | 144 | Wilson | 2,021 | Englemann spruce/Subalpine fir | Spectral | Boosted Regression Trees | 0.39 | anomalous snow-cover 1 year post-fire | 10.00000 | Positive | moderately ( P < 0.05) | ||
144-89 | anomalous snow-cover 3 year mean | 9.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-89 | anomalous precipitation 1 year post fire | 13.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-89 | anomalous precipitation 3 year mean | 20.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-89 | elevation | 22.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-89 | slope | 0.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-89 | aspect (southness) | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-89 | pre-fire composition | 9.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-89 | burn severity stdev | 11.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-89 | rdnbr | 6.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-96 | 144 | Wilson | 2,021 | Douglas Fir | Spectral | Boosted Regression Trees | 0.42 | anomalous snow-cover 1 year post-fire | 8.00000 | Negative | high (P <0.01) | ||
144-96 | anomalous snow-cover 3 years post-fire | 18.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-96 | anomalous precipitation | 26.00000 | Positive | high (P <0.01) | |||||||||
144-96 | elevation | 19.00000 | Negative | moderately ( P < 0.05) | |||||||||
144-96 | slope | 6.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-96 | aspect | 1.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-96 | pre-fire composition | 4.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-96 | burn severity stdev | 5.00000 | Positive | moderately ( P < 0.05) | |||||||||
144-96 | rdnbr | 5.00000 | Positive | moderately ( P < 0.05) | |||||||||
12-18 | 12 | Wooten | 2,022 | Mixed Conifer | Structural | Stem Density, Seedling / Sapling Precense | Correlation | 0.203 | post-fire minimum soil temperature | 7.38000 | Negative | high (P <0.01) | |
3917-124 | 3917 | Ziegler | 2,017 | Ponderosa Pine | Structural | Height | Generalized Linear Models | 0.021 | distance to edge | 1.59500 | Positive | high (P <0.01) | |
3917-124 | aspect | 1.05400 | Positive | Not ( P > 0.05) | |||||||||
3917-124 | slope | 1.35200 | Negative | Not ( P > 0.05) | |||||||||
3917-124 | tpi | 1.29400 | Positive | Not ( P > 0.05) | |||||||||
3917-124 | tpi | 1.29400 | Positive | Not ( P > 0.05) | |||||||||
3917-125 | 3917 | Ziegler | 2,017 | Lodgepole pine | Structural | Height | Generalized Linear Models | 0.271 | distance to edge | 3.65200 | Positive | Not ( P > 0.05) | |
3917-125 | aspect | 1.34800 | Positive | Not ( P > 0.05) | |||||||||
3917-125 | slope | 1.17700 | Negative | Not ( P > 0.05) | |||||||||
3917-125 | tpi | 1.19200 | Negative | Not ( P > 0.05) | |||||||||
3917-125 | tpi | 1.19200 | Negative | Not ( P > 0.05) | |||||||||
3917-126 | 3917 | Ziegler | 2,017 | Douglas fir | Structural | Height | Generalized Linear Models | 0.021 | distance to edge | 1.14200 | Positive | Not ( P > 0.05) | |
3917-126 | aspect | 1.59200 | Negative | very high (P < 0.001) | |||||||||
3917-126 | slope | 1.30500 | Negative | Not ( P > 0.05) | |||||||||
3917-126 | tpi | 1.02500 | Negative | Not ( P > 0.05) | |||||||||
3917-126 | tpi | 1.02500 | Negative | Not ( P > 0.05) | |||||||||
3917-66 | 3917 | Ziegler | 2,017 | Ponderosa Pine / Mixed Conifer | Structural | Regeneration Intensity (Spatial Clumping of Stems) | Cox Process Models | distance to edge | 119.74400 | Negative | very high (P < 0.001) | ||
3917-66 | aspect | 1.79300 | Positive | very high (P < 0.001) | |||||||||
3917-66 | slope | 13.34800 | Negative | very high (P < 0.001) | |||||||||
3917-66 | topographic position index | 1.58700 | Negative | Not ( P > 0.05) | |||||||||
3917-122 | 3917 | Ziegler | 2,017 | Lodgepole pine | Structural | Regeneration Intensity (Spatial Clumping of Stems) | Inhomogeneous Cox Process | Not applicable | distance to edge | 25.29400 | Negative | Not ( P > 0.05) | |
3917-122 | aspect | 3.81100 | Negative | Not ( P > 0.05) | |||||||||
3917-122 | slope | 630.66500 | Positive | very high (P < 0.001) | |||||||||
3917-122 | tpi | 2.70600 | Positive | Not ( P > 0.05) | |||||||||
3917-122 | tpi | 2.70600 | Positive | Not ( P > 0.05) | |||||||||
3917-123 | 3917 | Ziegler | 2,017 | Douglas fir | Structural | Regeneration Intensity (Spatial Clumping of Stems) | Inhomogeneous Cox Process | Not applicable | distance to edge | 265.84500 | Negative | very high (P < 0.001) | |
3917-123 | aspect | 3.19000 | Negative | high (P <0.01) | |||||||||
3917-123 | slope | 380.37200 | Positive | very high (P < 0.001) | |||||||||
3917-123 | tpi | 2.85700 | Negative | Not ( P > 0.05) | |||||||||
3917-123 | tpi | 2.85700 | Negative | Not ( P > 0.05) |