A | B | C | D | E | F | G | H | I | J | K | L | M | N | O | P | Q | R | S | T | U | V | W | X | Y | Z | |
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1 | Habitat | Source | Year(s) | Resolution | Coverage | Brief Description | Intensity | Buffer (m) | ||||||||||||||||||
2 | Eelgrass | WA Dept. of Natural Resources | 2001-2020 | n/a | WA state | Mapped eelgrass beds | Presence/ Absence | none | ||||||||||||||||||
3 | Kelp | WA Dept. of Natural Resources | 2017-2024 | 1 km shoreline segments | WA state | Linear extent of floating kelp along -6.1 m MLLW isobath | Presence/ Absence | none | ||||||||||||||||||
4 | ||||||||||||||||||||||||||
5 | Threat | Source | Year(s) | Resolution | Coverage | Brief Description [Stressors] | Intensity (Exposure) | Buffer (m) | ||||||||||||||||||
6 | Human activity (marine) | |||||||||||||||||||||||||
7 | Vessel Traffic | U.S. Coast Guard Automatic Identification System (AIS); marinecadastre.gov/ais/ | 2022 | 100 m grid | U.S. | Average number of vessels per day with AIS transponders [disturbance, contaminants, invasive species, water clarity] | Variable based on number of vessels/day quartile | none | ||||||||||||||||||
8 | Commercial shellfishing (eelgrass only) | WA Dept. of Natural Resources Commercial Harvest Sites | Active permits 11/2024 through 6/2025 | n/a | WA state | Sites with active commercial shellfish permits [disturbance, contaminants] | Presence/ Absence | none | ||||||||||||||||||
9 | Dredge disposal sites | US Army Corps of Engineers Disposal Site History; https://usace.contentdm.oclc.org/utils/getfile/collection/p266001coll1/id/10745 | n/a | n/a | Puget Sound and Strait of Juan de Fuca | “Disposal Site” locations [sediment, contaminants] | Presence/ Absence | none | ||||||||||||||||||
10 | Port facilities | Port locations; https://www.washingtonports.org/ourports-directory | n/a | n/a | WA state | Locations of seaports [disturbance, contaminants] | Presence/ Absence | 1000 | ||||||||||||||||||
11 | Human activity (terrestrial) | |||||||||||||||||||||||||
12 | Shoreline armoring | WA Dept. of Fish and Wildlife Beach Strategies Toolkit; https://beach-strategies-wdfw-hub.hub.arcgis.com/ | 2017 | 0.01 - 5,400 m shoreline segments | WA Salish Sea | Locations of armored shoreline [disturbance] | Presence/ Absence | 1000 | ||||||||||||||||||
13 | Oil/gas facilities | WA Dept. of Ecology Spills Program Regulated Facilities | n/a | n/a | WA state | Locations of oil/gas facilities [contaminants] | Presence/ Absence | 1000 | ||||||||||||||||||
14 | Land cover (impervious surface) | National Landcover Dataset Fractional Impervious Surface | 2023 | 30m | Continental US | % impervious surface coverage of watershed [nutrients, sediments, contaminants] | Variable based on % cover quartile* | Variable based on river flow† | ||||||||||||||||||
15 | Land use (industrial) | WA Dept. of Commerce General Land Use Dataset | 2022 | n/a | Puget Sound Watershed | % industrial land use (heavy and light) of watershed [sediments, contaminants] | Variable based on % cover quartile* | Variable based on river flow† | ||||||||||||||||||
16 | Water quality | |||||||||||||||||||||||||
17 | Temperature | Salish Sea Model** | 2014 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled dry season average daily maximum temperature in the surface layer [temperature] | Variable based on value quartile* | none | ||||||||||||||||||
18 | Salinity | Salish Sea Model** | 2014 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled wet season average daily minimum salinity in the surface layer [salinity] | Variable based on value quartile* | none | ||||||||||||||||||
19 | High nutrients | Salish Sea Model** | 2014 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled wet season average daily maximum dissolved inorganic nitrogen (nitrate + ammonium) concentration in the water column [nutrients, algal competition] | Variable based on value quartile* | none | ||||||||||||||||||
20 | Low nutrients (kelp only) | Salish Sea Model** | 2014 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled dry season average daily minimum dissolved inorganic nitrogen (nitrate + ammonium) concentration in the surface layer [nutrients] | Variable based on value quartile* | none | ||||||||||||||||||
21 | Riverine influence† | Washington State Department of Ecology** | 18-year Climatology | 130 rivers entering Puget Sound | WA Salish Sea | Average annual river flow [sediment, contaminants, salinity] | Variable based on river flow quartile* | Variable based on river flow† | ||||||||||||||||||
22 | Riverine flashiness | Washington State Department of Ecology** | 18-year Climatology | 130 rivers entering Puget Sound | WA Salish Sea | River flow variability [sediment, contaminants, salinity] | Variable based on river variability quartile* | Variable based on river flow† | ||||||||||||||||||
23 | Riverine nutrients | Washington State Department of Ecology** | 18-year Climatology | 130 rivers entering Puget Sound | WA Salish Sea | Average annual dissolved inorganic nitrogen (nitrate + ammonium) load [nutrients, algal competition, water clarity] | Variable based on load quartile* | Variable based on river flow† | ||||||||||||||||||
24 | Wastewater Treatment Plant nutrients | Washington State Department of Ecology** | 18-year Climatology | 89 outfalls entering Puget Sound | WA Salish Sea | Average annual dissolved inorganic nitrogen (nitrate + ammonium) load [nutrients, algal competition, water clarity] | Variable based on load quartile* | Variable based on WWTP flow§ | ||||||||||||||||||
25 | Climate Change | |||||||||||||||||||||||||
26 | Temperature | Khangaonkar et al. 2021: https://www.sciencedirect.com/science/article/pii/S0304380020304786 | 2095 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled dry season average daily maximum temperature in the surface layer [temperature] | Variable based on value quartile* | none | ||||||||||||||||||
27 | Salinity | Khangaonkar et al. 2021: https://www.sciencedirect.com/science/article/pii/S0304380020304786 | 2095 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled wet season average daily minimum salinity in the surface layer [salinity] | Variable based on value quartile* | none | ||||||||||||||||||
28 | High nutrients | Khangaonkar et al. 2021: https://www.sciencedirect.com/science/article/pii/S0304380020304786 | 2095 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled wet season average daily maximum dissolved inorganic nitrogen (nitrate + ammonium) concentration in the water column [nutrients, algal competition] | Variable based on value quartile* | none | ||||||||||||||||||
29 | Low nutrients (kelp only) | Khangaonkar et al. 2021: https://www.sciencedirect.com/science/article/pii/S0304380020304786 | 2095 | 100 m - 3,000 m unstructured grid | Salish Sea, Outer Coast | Modeled dry season average daily minimum dissolved inorganic nitrogen (nitrate + ammonium) concentration in the surface layer [nutrients] | Variable based on value quartile* | none | ||||||||||||||||||
30 | Sea Level Rise | Miller et al. 2018: https://cig.uw.edu/publications/projected-sea-level-rise-in-washington-state-a-2018-assessment/ | 2100 | 3 - 57,000 m shoreline segments | WA coastline | Magnitude of projected SLR for 2100 (RCP 8.5, 50th percentile projection) [light, coastal squeeze] | Variable based on value quartile* | none | ||||||||||||||||||
31 | * Intensity scores were determined using a quartile approach: bottom quartile of values = low (1), middle two quartiles = med (2), upper quartile = high (3), except for the salinity threat (eelgrass and kelp) and the low nutrient stressor (kelp) where the scores applied to quartiles were reversed (bottom quartile = high and upper quartile = low) | |||||||||||||||||||||||||
32 | ** Climatology source data available at: https://fortress.wa.gov/ecy/ezshare/EAP/SalishSea/SalishSeaModelBoundingScenarios.html | |||||||||||||||||||||||||
33 | † The river flow climatology quartile was used to determine the buffer size for riverine based threats (Land Use, Land Cover, Riverine nutrients, and Riverine influence) as follows: Low (< 25th percentile) = 2,500 m, Medium (25th-75th percentile) = 5,000 m, and High (> 75th percentile) = 10,000 m buffer | |||||||||||||||||||||||||
34 | § The wastewater treatment plant flow climatology quartile was used to determine the buffer size for Wastewater Treatment Plant nutrients as follows: Low (< 25th percentile) = 1,000 m, Medium (25th-75th percentile) = 2,500 m, and High (> 75th percentile) = 5,000 m buffer | |||||||||||||||||||||||||
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