| Layer | Description |
|---|---|
| hli_cool_slopes_pnw | Heat Load Index - Cool Slopes, raw area of cool slopes per HUC in km2. |
| max_chg_40 | Max projected change in stream flow per HUC comparing current and 2040s time periods. |
| min_cng_40 | Min projected change in stream flow per HUC comparing current and 2040s time periods. |
| index_cng_40 | Projected streamflow change index - calculated as the mean percent change in streamflow based on sum of stream segment lengths times flow changes divided by total stream length in a HUC |
| ergo_valleys_pnw | Theobald Ergo land forms Valley – is proportion of HUC |
| lc16evc_pnw | Mean forest canopy cover at the HUC12 level |
| Theobald_HM_270 | Theobald Human Footprint |
| TNC_permeability | Permeability index |
| TNC_Topoclimate | TNC Topoclimatic diversity |
| topo7x7x1kmrao_LAEA | Mean topographic complexity, defined as regions with a large variability in elevation and aspect in close proximity, per HUC |
| prop345.index | Current Wildfire Hazard Index. Area of HUC classified as hazard level 3 (moderate), 4 (high), or 5 (very high) multiplied by 3, 4, , and 5 as weights repectively and divided by the total HUC area. |
| Davis_MidCent_PctChange | Projected % change in fire suitability for forested areas - mid-century time period |
| Davis_EndCent_PctChange | Projected % change in fire suitability for forested areas - end-of-century time period |
| prs.ref | Percent Replacement Severity (prs), raw value reference time period. |
| prs.55.cng | prs 2055 time period and change metric (2055 – reference) |
| fri.ref | Fire return interval |
| fri.55.cng | Fire return interval 2055 change |
| fri.2055 | Fire return interval 2055 raw value |
| fri.2085 | Fire return interval 2085 raw value |
| prs.2055 | Percent Replacement Severity, raw value 2055s |
| prs.2085 | Percent Replacement Severity, raw value 2085s |
| fri.85.cng | Fire return interval 2085 change |
| fri.55.perc.cng | Fire return interval 2055 % change |
| fri.85.perc.cng | Fire return interval 2085 % change |
| prs.85.cng | Percent Replacement Severity 2085 change |
| prs.55.perc.cng | Percent Replacement Severity 2055 % change |
| prs.85.perc.cng | Percent Replacement Severity 2085 % change |
| cssqkm | total area (Square km) of cool-facing slopes in the HUC |
| cs.prop | Proportion of huc classified as cool-facing slope |
| cs.val.prop | proportion of huc classified as cool-facing slope OR valley |
| medhist | Median Stream Temperature within a HUC. Historical. |
| med2040 | Median Stream Temperature within a HUC. Projected 2040s |
| med2080 | Median Stream Temperature within a HUC. Projected 2080s |
| change_in_snowpack | Median changes in snowpack as % of Snow Water Equivalent (SWE) |
| NonForest2Forest_2050 | Mean non forest to forest conversion 2050 |
| Resistance_and_Resilience | Median Resistance and Resilience |
| North_American_Climate_Refugia | North American Climate Refugia probability |
| drought_refugia_median | Median soil drought probability |
Refugia
General refugia analysis
Deliverable: Leverage existing data for physical climate-change exposure, environmental diversity (e.g., locations with a high diversity of landform types, topographic, soil, and/or local climatic conditions and subsequently a high potential for microrefugia), and climatic velocity to identify locations within Washington that have high refugia potential based on their physical characteristics filter strategies seek to conserve either key sites as determined by natural elements unaffected by climate change, or sites with low climate velocity that are expected to be refugia for climate-displaced species. Compare these physical refugia results with (1) species specific refugia modeling work from previous project and (2) Stralberg et al.’s (2018) tree and bird macrorefugia index to identify the level of agreement between the two efforts.
Data Deliverables
Individual data layers for [physical] refugia showing locations with high to low refugia potential.
Here 33 layers were used to incorporate the General Refugia. The layers represent continuous values, below is the table describing the 33 layers.
Showing the list of the variables with summary statistics, note that areaacres and areasqkm are for information only.
| id | mean | median | min | max | range | se | |
|---|---|---|---|---|---|---|---|
| hli_cool_slopes_pnw | 1 | 2688.49 | 2427.00 | 9.00 | 8151.00 | 8142.00 | 43.48 |
| max_chg_40 | 2 | -7.18 | 0.00 | -53.87 | 10.43 | 64.30 | 0.31 |
| min_cng_40 | 3 | -30.68 | -26.01 | -81.67 | 1.52 | 83.19 | 0.56 |
| index_cng_40 | 4 | -20.21 | -15.86 | -71.29 | 3.89 | 75.17 | 0.42 |
| ergo_valleys_pnw | 5 | 0.13 | 0.13 | 0.01 | 0.74 | 0.72 | 0.00 |
| lc16evc_pnw | 6 | 39.05 | 43.18 | 0.00 | 75.52 | 75.51 | 0.57 |
| Theobald_HM_270 | 7 | 0.18 | 0.12 | 0.00 | 0.89 | 0.89 | 0.00 |
| TNC_permeability | 8 | 0.61 | 0.66 | 0.01 | 1.00 | 0.99 | 0.01 |
| TNC_Topoclimate | 9 | 0.35 | 0.36 | 0.22 | 0.48 | 0.27 | 0.00 |
| topo7x7x1kmrao_LAEA | 10 | 179.33 | 167.93 | 6.18 | 585.55 | 579.37 | 3.28 |
| prop345.index | 11 | 0.31 | 0.19 | 0.00 | 0.99 | 0.99 | 0.01 |
| Davis_MidCent_PctChange | 12 | 45.15 | 42.13 | 0.00 | 126.42 | 126.42 | 0.53 |
| Davis_EndCent_PctChange | 13 | 99.55 | 95.50 | 0.00 | 263.21 | 263.21 | 1.38 |
| prs.ref | 14 | 54.84 | 47.83 | 10.04 | 98.00 | 87.96 | 0.66 |
| prs.55.cng | 15 | 3.42 | 2.48 | -50.69 | 52.27 | 102.97 | 0.36 |
| fri.ref | 16 | 367.49 | 368.05 | 16.39 | 993.52 | 977.13 | 8.08 |
| fri.55.cng | 17 | -28.88 | -7.27 | -482.70 | 365.41 | 848.10 | 2.62 |
| fri.2055 | 18 | 338.61 | 356.71 | 23.30 | 964.54 | 941.24 | 7.19 |
| fri.2085 | 19 | 292.44 | 272.08 | 24.95 | 932.41 | 907.46 | 6.19 |
| prs.2055 | 20 | 58.26 | 57.70 | 14.15 | 97.15 | 83.00 | 0.66 |
| prs.2085 | 21 | 59.00 | 60.31 | 11.05 | 98.00 | 86.95 | 0.63 |
| fri.85.cng | 22 | -75.05 | -40.75 | -641.51 | 823.89 | 1465.40 | 4.20 |
| fri.55.perc.cng | 23 | 3.58 | -5.29 | -87.96 | 676.95 | 764.91 | 1.25 |
| fri.85.perc.cng | 24 | 5.69 | -15.81 | -90.88 | 1065.66 | 1156.54 | 2.85 |
| prs.85.cng | 25 | 4.16 | 3.48 | -84.89 | 76.08 | 160.97 | 0.63 |
| prs.55.perc.cng | 26 | 10.92 | 4.22 | -57.37 | 241.12 | 298.50 | 0.88 |
| prs.85.perc.cng | 27 | 22.36 | 6.32 | -88.49 | 492.29 | 580.77 | 1.85 |
| cssqkm | 28 | 26.88 | 24.27 | 0.09 | 81.51 | 81.42 | 0.43 |
| cs.prop | 29 | 0.30 | 0.30 | 0.00 | 0.74 | 0.74 | 0.00 |
| cs.val.prop | 30 | 0.43 | 0.43 | 0.03 | 0.79 | 0.76 | 0.00 |
| medhist | 31 | 12.39 | 12.62 | 3.75 | 22.39 | 18.64 | 0.08 |
| med2040 | 32 | 13.82 | 14.05 | 5.26 | 23.90 | 18.64 | 0.08 |
| med2080 | 33 | 14.78 | 15.03 | 6.25 | 24.89 | 18.64 | 0.08 |
| change_in_snowpack | 34 | -65.31 | -99.00 | -100.00 | 0.00 | 100.00 | 1.22 |
| NonForest2Forest_2050 | 35 | 0.06 | 0.01 | 0.00 | 0.94 | 0.94 | 0.00 |
| Resistance_and_Resilience | 36 | 0.53 | 0.00 | 0.00 | 3.00 | 3.00 | 0.03 |
| North_American_Climate_Refugia | 37 | 0.12 | 0.00 | 0.00 | 1.00 | 1.00 | 0.01 |
| drought_refugia_median | 38 | 23.19 | 2.00 | 0.00 | 100.00 | 100.00 | 0.95 |
Plot the density distributions of all the layers
Create the layers for distribution
Sample forest cover layer that twill be exported
[1] "Writing refugia layer.hli_cool_slopes_pnw"
[1] "Writing refugia layer.max_chg_40"
[1] "Writing refugia layer.min_cng_40"
[1] "Writing refugia layer.index_cng_40"
[1] "Writing refugia layer.ergo_valleys_pnw"
[1] "Writing refugia layer.lc16evc_pnw"
[1] "Writing refugia layer.Theobald_HM_270"
[1] "Writing refugia layer.TNC_permeability"
[1] "Writing refugia layer.TNC_Topoclimate"
[1] "Writing refugia layer.topo7x7x1kmrao_LAEA"
[1] "Writing refugia layer.prop345.index"
[1] "Writing refugia layer.Davis_MidCent_PctChange"
[1] "Writing refugia layer.Davis_EndCent_PctChange"
[1] "Writing refugia layer.prs.ref"
[1] "Writing refugia layer.prs.55.cng"
[1] "Writing refugia layer.fri.ref"
[1] "Writing refugia layer.fri.55.cng"
[1] "Writing refugia layer.fri.2055"
[1] "Writing refugia layer.fri.2085"
[1] "Writing refugia layer.prs.2055"
[1] "Writing refugia layer.prs.2085"
[1] "Writing refugia layer.fri.85.cng"
[1] "Writing refugia layer.fri.55.perc.cng"
[1] "Writing refugia layer.fri.85.perc.cng"
[1] "Writing refugia layer.prs.85.cng"
[1] "Writing refugia layer.prs.55.perc.cng"
[1] "Writing refugia layer.prs.85.perc.cng"
[1] "Writing refugia layer.cssqkm"
[1] "Writing refugia layer.cs.prop"
[1] "Writing refugia layer.cs.val.prop"
[1] "Writing refugia layer.medhist"
[1] "Writing refugia layer.med2040"
[1] "Writing refugia layer.med2080"
[1] "Writing refugia layer.change_in_snowpack"
[1] "Writing refugia layer.NonForest2Forest_2050"
[1] "Writing refugia layer.Resistance_and_Resilience"
[1] "Writing refugia layer.North_American_Climate_Refugia"
[1] "Writing refugia layer.drought_refugia_median"
{r} # #| message: false # #| warning: false # #| echo: false # # # Load shapefile # wwf_shp <- st_read("./data/GIS/Combined/allhucsforestcover.shp", stringsAsFactors = F) # # # Rasterize biome field and write to disk # # sfvect <- terra::vect("./data/GIS/Combined/allhucsforestcover.shp") # r <- terra::rast(sfvect, ncols=750, nrows=750) # fp <- terra::rasterize(sfvect,r) # terra::writeRaster(fp, "./data/GIS/Combined/allhucsforestcover.tiff",overwrite=TRUE) # #
Integrated refugia data layer(s) showing locations with high priority across multiple refugia metrics and approaches.
Three refugia maps -Aquatic, Sage and Forest with predefined list of layers
Aquatic Refugia Map -
Aquatic or Amphibia Includes the salamanders, frogs, toads, and caecilians.
Here we use the below layers
Historic median stream temperatures (medhist)
Median stream temperatures 2040s (med2040)
Median stream temperatures 2080s (med2080)
Cool Slopes Proportion (cs.prop)
Stream flow loss (index_cng_40)
Forest canopy (lc16evc_pnw)
Show the distribution of 7 variables
Show the quartiles
Plot the Aquatic refugia map - criteria median stream temperature below 10 degrees Celsius, proportion of cool slopes at HUC level more than 40%, flow loss less than 30%, forest canopy more than 40%, and drought refugia less than 30%.
Sage Refugia Map -
Sage Includes the Sage Grouse …
Here we use the below layers
TNC Permeability (TNC_permeability)
Current Fire WHP (prop345_in)
NonForest-2-Forest Conversion 2055 (NonForest2Forest_2050)
Resistance and Resilience (Resistance_and_Resilience)
Drought refugia (drought_refugia_median)
Show the distribution of 6 variables
Show the quartiles
Plot the Sage refugia map - TNC Permeability of 0.8 or higher, and Current Wildfire Hazard Index of 0.2 or lower
Forest Refugia Map -
Forest Includes the Fisher, White headed wood-pecker …
Here we use the below layers
- Mean forest cover per HUC (%) (lc16evc_pnw)
- TNC Permeability (TNC_permeability)
- Current Fire WHP (prop345_in)
- Proportion of HUC classified as cool slopes (cs.prop)
- Drought refugia (drought_refugia_median)
- Change in snowpack % SWE
- North American Climate Refugia (North_American_Climate_Refugia)
Show the distribution of 6 variables
Show the quartiles
Plot the Forest refugia map - TNC Permeability of 0.8 or higher, Current Wildfire Hazard Index of 0.8 or higher, proportion of cool slopes at HUC level more than 40%, forest canopy more than 40% and drought probability less than 40%.
Filtered refugia data by land cover/land use/land ownership – which locations have high refugia potential and high landscape integrity/good habitat potential otherwise?
- We will produce for e.g., % of refugia found in public, [private lands]
- % Of refugia that are in public or private lands
TODO - Add information on whhere the layers came from - Add total area
First using 25% threshold (atleast 25% of the HUC is protected)
At 25%, given the criteria above for the refugia’s, there are 363 HUCs that are in protected (public, state or conservancy) in WA. 8 HUCs that are in Aquatic refugia are protected, 0 HUCs that are in Sage refugia are protected, and 32 HUCs that are in Forest refugia are protected. Total HUCs that are protected are 11% of identified refugiaHUCs.
Using 50% threshold (atleast 50% of the HUC is protected)
At 50%, given the criteria above for the refugia’s, there are 271 HUCs that are in protected (public, state or conservancy) in WA. 8 HUCs that are in Aquatic refugia are protected, 0 HUCs that are in Sage refugia are protected, and 30 HUCs that are in Forest refugia are protected. Total HUCs that are protected are 14% of total protected HUCs.
Using 75% threshold (atleast 75% of the HUC is protected)
At 75%, given the criteria above for the refugia’s, there are 674 HUCs that are in protected (public, state or conservancy) in WA. 11 HUCs that are in Aquatic refugia are protected, 17 HUCs that are in Sage refugia are protected, and 6 HUCs that are in Forest refugia are protected. Total HUCs that are protected are 5% of the total protected HUCs.
Locations having high landscape integrity
Done by calculating average Theobald value per huc and generating a bar chart comparing refugia hucs to non-refugia hucs based on average Theoboald value. Do this for all three general refugia types. (will probably need to use only forest, sage, and aquatic hucs in the comparisons– if possible).
Analysis of the number and types of species that could be potentially served by different refugia locations by overlaying locations with high refugia potential over current range distributions of priority species and habitats (either PHS or SGCN).
We will take the generalized layers of refugia and overlay habit maps of species given by WDFW Use the 100+ species , and map it to one of the three At the HUC level - # of species Species - How many HUCs (all three refugia) for a Species , make a table.
A total of 83 species are there
Number of HUCs that overlaps each type of Refugia and Species potential ranges
| Refugia | nohucs |
|---|---|
| Aquatic | 161 |
| Forest | 825 |
| Sage | 326 |
Number of Species served by each Refugia
| Refugia | NoOfSpecies |
|---|---|
| Aquatic | 31 |
| Forest | 55 |
| Sage | 52 |
Number of HUCs for species that overlaps with obtained refugias (Aquatic, Sage and Forest)
| index | Common_Name | Scientific_Name | Aquatic | Sage | Forest |
|---|---|---|---|---|---|
| 1 | Spotted sandpiper | Actitis macularia | 0 | 1 | 10 |
| 2 | Clark's grebe | Aechmophorus clarkii | 0 | 3 | 0 |
| 3 | Western grebe | Aechmophorus occidentalis | 0 | 5 | 0 |
| 4 | Sagebrush Sparrow | Amphispiza nevadensis | 0 | 6 | 1 |
| 5 | Tiger salamander | Ambystoma tigrinum | 0 | 9 | 1 |
| 6 | Western toad | Anaxyrus boreas | 9 | 7 | 47 |
| 7 | Woodhouse's toad | Anaxyrus woodhousii | 0 | 4 | 0 |
| 8 | Golden eagle | Aquila chrysaetos | 4 | 10 | 28 |
| 9 | Rocky Mountain Tailed Frog | Ascaphus montanus | 0 | 1 | 1 |
| 10 | Burrowing owl | Athene cunicularia | 0 | 11 | 1 |
| 11 | Cascade red fox | Vulpes vulpes cascadensis | 4 | 0 | 3 |
| 12 | Side-blotched lizard | Uta stansburiana | 0 | 4 | 0 |
| 13 | Washington ground squirrel | Urocitellus washingtoni | 0 | 5 | 0 |
| 14 | Townsend's Ground Squirrel - nancyae | Urocitellus townsendii nancyae | 0 | 2 | 0 |
| 15 | Grizzly bear | Ursus arctos | 6 | 0 | 16 |
| 16 | Columbian Sharp-tailed Grouse | Tympanuchus phasianellus | 0 | 7 | 0 |
| 17 | Brush prairie pocket gopher-Northern | Thomomys talpoides douglasii | 0 | 0 | 0 |
| 18 | Mazama (Western) pocket gopher | Thomomys mazama | 0 | 0 | 6 |
| 19 | American Badger | Taxidea taxus | 0 | 13 | 4 |
| 20 | Northern Spotted Owl | Strix occidentalis | 9 | 1 | 46 |
| 21 | Great gray owl | Strix nebulosa | 1 | 3 | 6 |
| 22 | Valley silverspot | Speyeria zerene bremnerii | 1 | 0 | 16 |
| 23 | Pygmy nuthatch | Sitta pygmaea | 3 | 9 | 4 |
| 24 | Western bluebird | Sialia mexicana | 3 | 0 | 20 |
| 25 | Slender-billed white-breasted nuthatch | Sitta carolinensis aculeata | 0 | 0 | 0 |
| 26 | Western gray squirrel | Sciurus griseus | 2 | 2 | 3 |
| 27 | Sagebrush lizard | Sceloporus graciosus | 0 | 10 | 2 |
| 28 | Olympic torrent salamander | Rhyacotriton olympicus | 0 | 0 | 19 |
| 29 | Columbia torrent salamander | Rhyacotriton kezeri | 0 | 0 | 0 |
| 30 | Cascade torrent salamander | Rhyacotriton cascadae | 2 | 0 | 5 |
| 31 | Woodland caribou | Rangifer tarandus | 0 | 0 | 0 |
| 32 | Oregon spotted frog | Rana pretiosa | 0 | 0 | 9 |
| 33 | Northern leopard frog | Rana pipiens | 0 | 1 | 0 |
| 34 | Columbia spotted frog | Rana luteiventris | 6 | 9 | 6 |
| 35 | Purple martin | Progne subis | 0 | 0 | 10 |
| 36 | Mardon skipper | Polites mardon | 0 | 0 | 0 |
| 37 | Oregon vesper sparrow | Pooecetes gramineus affinis | 0 | 0 | 4 |
| 38 | Red-necked grebe | Podiceps grisegena | 0 | 6 | 0 |
| 39 | Van dyke's salamander | Plethodon vandykei | 3 | 0 | 20 |
| 40 | Larch mountain salamander | Plethodon larselli | 3 | 0 | 6 |
| 41 | Dunn's salamander | Plethodon dunni | 0 | 0 | 0 |
| 42 | White-headed woodpecker | Picoides albolarvatus | 3 | 5 | 4 |
| 43 | Pygmy Short-horned Lizard | Phrynosoma douglasii | 0 | 10 | 1 |
| 44 | American white pelican | Pelecanus erythrorhynchos | 0 | 8 | 0 |
| 45 | Western screech-owl | Otus kennicottii | 8 | 0 | 42 |
| 46 | Flammulated owl | Otus flammeolus | 3 | 5 | 4 |
| 47 | Sage thrasher | Oreoscoptes montanus | 0 | 9 | 2 |
| 48 | Columbian white-tailed deer | Odocoileus virginianus leucurus | 0 | 0 | 0 |
| 49 | American Pika | Ochotona princeps | 9 | 2 | 27 |
| 50 | Shaw Island Townsend's vole | Microtus townsendii pugeti | 0 | 0 | 0 |
| 51 | Kincaid meadow vole | Microtus pennsylvanicus kincaidi | 0 | 6 | 0 |
| 52 | Lewis' woodpecker | Melanerpes lewis | 0 | 6 | 3 |
| 53 | Striped whipsnake | Masticophis taeniatus | 0 | 3 | 0 |
| 54 | Fisher | Martes pennanti | 9 | 2 | 46 |
| 55 | Olympic marmot | Marmota olympus | 0 | 0 | 18 |
| 56 | Lynx | Lynx canadensis | 5 | 4 | 11 |
| 57 | White-tailed jackrabbit | Lepus townsendii | 0 | 13 | 2 |
| 58 | Black-tailed jackrabbit | Lepus californicus | 0 | 12 | 2 |
| 59 | Silver-haired bat | Lasionycteris noctivagans | 9 | 13 | 47 |
| 60 | Loggerhead shrike | Lanius ludovicianus | 0 | 8 | 0 |
| 61 | Hoary bat | Lasiurus cinereus | 9 | 13 | 47 |
| 62 | Desert Nightsnake | Hypsiglena chlorophaea | 0 | 10 | 2 |
| 63 | Bald eagle | Haliaeetus leucocephalus | 4 | 12 | 42 |
| 64 | Wolverine | Gulo gulo | 9 | 4 | 22 |
| 65 | Common loon | Gavia immer | 3 | 0 | 13 |
| 66 | Peregrine falcon | Falco peregrinus | 9 | 12 | 47 |
| 67 | Spotted bat | Euderma maculatum | 1 | 5 | 1 |
| 68 | Streaked horned lark | Eremophila alpestris strigata | 0 | 0 | 0 |
| 69 | Ring-necked Snake | Diadophis punctatus | 0 | 1 | 0 |
| 70 | Cope's giant salamander | Dicamptodon copei | 2 | 0 | 18 |
| 71 | Townsend's Big-eared Bat | Corynorhinus townsendii | 9 | 13 | 47 |
| 72 | Sharp-tailed Snake | Contia tenuis | 0 | 1 | 1 |
| 73 | Yellow-billed cuckoo | Coccyzus americanus | 0 | 2 | 2 |
| 74 | Greater Sage-grouse | Centrocercus urophasianus | 0 | 4 | 0 |
| 75 | Gray wolf | Canis lupus | 4 | 4 | 7 |
| 76 | Ferruginous hawk | Buteo regalis | 0 | 9 | 1 |
| 77 | Marbled murrelet | Brachyramphus marmoratus | 9 | 0 | 43 |
| 78 | Pygmy rabbit | Brachylagus idahoensis | 0 | 1 | 0 |