Date: 20-Dec-21
This page has been converted from its original source. View the original 2022 & 2023 Work Plan Scoring Compilation w Ranking Summary_FINAL (PDF)
7 New* & Updated Projects listed from West to East
| HWS ID | Title | Category | Narrative Link |
|---|---|---|---|
| 21001* | Expansion of Shipwreck Point NRCA | Capital | SRP Project |
| 19103.1 | Johnson Creek Triple Culverts Replacement | Capital | SRP Project |
| 09001.2 | Little Hoko River Large Wood Restoration | Capital | SRP Project |
| 10080.3 | Lyre River Protection and Restoration | Capital | SRP Project |
| 11088.2 | Ennis Creek Barrier Replacement | Capital | SRP Project |
| 09027.2 | Siebert Creek Ecosystem Protection & Restoration | Capital | SRP Project |
| 12098.1 | Dungeness River Instream Flow Restoration-Storage | Capital | SRP Project |
43 Projects Already on the Work Plan (In Rank Order)
| PRISM ID | Title |
|---|---|
| 09092.1 | Dungeness River Floodplain Restoration |
| 09055.1 | Elwha River Estuary/Nearshore Conservation and Restoration |
| 09030.1 | Dungeness River Riparian Habitat Protection |
| 14106 | Elwha Acquisition and Restoration Project |
| 16103 | Indian Creek Habitat Restoration Project |
| 09029.1 | Dungeness River Large Wood Restoration |
| 13102 | Little River LWD Project |
| 09032.1 | Dungeness Drift Cell Conservation |
| 09031.1 | Dungeness River Riparian Restoration |
| 16102 | Morse Creek Acquisition & Restoration |
| 09093 | North Sequim Bay Drift Cell Conservation Project |
| 13101.1 | Lower Hoko Acquisition and Restoration Project |
| 09009.1 | Pysht River Salt Marsh Estuary Restoration Project |
| 12096 | Acquisition of Priorities identified in the HCP |
| 09091 | Dungeness River Instream Flow Restoration-Irrigation Efficiencies |
| 09011 | Twin River Acquisition |
| 09013 | Lower Salt Creek Restoration and Protection |
| 09086.1 | Pysht Floodplain Acquisition and Restoration |
| 11087 | Elwha River Revegetation Project |
| 11085.1 | Pysht River Watershed Wood Restoration Phase 4 Project |
| 14107 | Sequim Bay Shoreline Restoration |
| 09046 | Washington Harbor Habitat Protection Project |
| 09039.2 | McDonald Creek Barrier Removal and Channel Restoration |
| 09053 | Clallam Watertype Inventory and Assessment |
| 19104 | Lyre River Habitat Restoration |
| 19105 | Upper Cowan Ranch LWD |
| 10079 | Lower Morse Creek Feasibility Study |
| 09003 | WRIA 19 Riparian Restoration |
| 11090.1 | Siebert Creek Large Wood Restoration |
| 11084 | Upper Hoko LWD Restoration Project |
| 10078.1 | McDonald Creek Large Wood Restoration |
| 09026 | Morse Creek Property Acquisition |
| 19102 | Hoko Culvert 80001279 Replacement |
| 09015 | Salt Creek Final Fish Passage Corrections Project |
| 11094 | Chicken Coop Road Culvert Replacement Project |
| 09015.1 | Kreaman Creek, Trib. To Salt Creek |
| 09005 | Sekiu Mainstem (RM 2-5) LWD Restoration |
| 09021 | Valley Creek Restoration Phase 3 |
| 19101 | Fish Passage Corrections on Joyce-Piedmont Road |
Projects Listed in Rank Order (7 Additional Projects in Bold)
- Cap Max Possible Score = 206.96
- Non-Cap Max Possible Score = 151.80
| Rank | Project ID | Title | Category | Weighted Mean Score | Normalized Score |
|---|---|---|---|---|---|
| 1 | 09092.1 | Dungeness River Floodplain Restoration | Capital | 188.27 | 0.910 |
| 2 | 09055.1 | Elwha River Estuary/Nearshore Conservation and Restoration | Capital | 181.45 | 0.877 |
| 3 | 09030.1 | Dungeness River Riparian Habitat Protection | Capital | 177.34 | 0.857 |
| 4 | 14106 | Elwha Acquisition and Restoration Project | Capital | 175.51 | 0.848 |
| 5 | 16103 | Indian Creek Habitat Restoration Project | Capital | 174.96 | 0.845 |
| 6 | 09029.1 | Dungeness River Large Wood Restoration | Capital | 174.44 | 0.843 |
| 7 | 13102 | Little River LWD Project | Capital | 173.07 | 0.836 |
| 8 | 09032.1 | Dungeness Drift Cell Conservation | Capital | 173.05 | 0.836 |
| 9 | 09031.1 | Dungeness River Riparian Restoration | Capital | 170.77 | 0.825 |
| 10 | 16102 | Morse Creek Acquisition & Restoration | Capital | 169.29 | 0.818 |
| 11 | 09093 | North Sequim Bay Drift Cell Conservation Project | Capital | 168.80 | 0.816 |
| 12 | 13101.1 | Lower Hoko Acquisition and Restoration Project | Capital | 168.29 | 0.813 |
| 13 | 09009.1 | Pysht River Salt Marsh Estuary Restoration Project | Capital | 167.66 | 0.810 |
| 14 | 09016.2 | Elwha River ELJ Project | Capital | 167.52 | 0.809 |
| 15 | 16104 | Elwha Hot Springs Road Restoration | Capital | 166.08 | 0.802 |
| 16 | 12096 | Acquisition of Priorities identified in the HCP | Capital | 165.70 | 0.801 |
| 17 | 09091 | Dungeness River Instream Flow Restoration-Irrigation Efficiencies | Capital | 163.48 | 0.790 |
| 18 | 09011 | Twin River Acquisition | Capital | 162.15 | 0.783 |
| 19 | 09013 | Lower Salt Creek Restoration and Protection | Capital | 161.50 | 0.780 |
| 20 | 09086.1 | Pysht Floodplain Acquisition and Restoration | Capital | 159.95 | 0.773 |
| 21 | 11087 | Elwha River Revegetation Project | Capital | 158.93 | 0.768 |
| 22 | 11085.1 | Pysht River Watershed Wood Restoration Phase 4 Project | Capital | 156.98 | 0.759 |
| 23 | 14107 | Sequim Bay Shoreline Restoration | Capital | 156.73 | 0.757 |
| 26 | 09053 | Clallam Watertype Inventory and Assessment | Non- | 112.37 | 0.740 |
| 27 | 10080.3 | Lyre River Protection and Restoration | Capital Capital | 153.03 | 0.739 |
| 28 | 19104 | Lyre River Habitat Restoration | Capital | 152.94 | 0.739 |
| 29 | 19105 | Upper Cowan Ranch LWD | Capital | 152.33 | 0.736 |
| 30 | 10079 | Lower Morse Creek Feasibility Study | Capital | 152.17 | 0.735 |
| 31 | 12098.1 | Dungeness River Instream Flow Restoration-Storage | Capital | 150.28 | 0.726 |
| 32 | 09003 | WRIA 19 Riparian Restoration | Capital | 149.78 | 0.724 |
| 33 | 11090.1 | Siebert Creek Large Wood Restoration | Capital | 149.15 | 0.721 |
| 34 | 11084 | Upper Hoko LWD Restoration Project | Capital | 148.44 | 0.717 |
| 35 | 10078.1 | McDonald Creek Large Wood Restoration | Capital | 146.66 | 0.709 |
| 36 | 11088.2 | Ennis Creeek Barrier Replacement | Capital | 145.01 | 0.701 |
| 37 | 09001.2 | Little Hoko River Large Wood Restoration | Capital | 142.66 | 0.689 |
| 38 | 09027.2 | Siebert Creek Ecosystem Protection & Restoration | Capital | 141.93 | 0.686 |
| 39 | 09026 | Morse Creek Property Acquisition | Capital | 138.29 | 0.668 |
| 40 | 19102 | Hoko Culvert 80001279 Replacement | Capital | 136.34 | 0.659 |
| 41 | 19103.1 | Johnson Creek Triple Culverts Replacement | Capital | 136.26 | 0.658 |
| 42 | 21001 | Expansion of Shipwreck Point NRCA | Capital | 133.63 | 0.646 |
| 43 | 09015 | Salt Creek Final Fish Passage Corrections Project | Capital | 133.57 | 0.645 |
| 44 | 11094 | Chicken Coop Road Culvert Replacement Project | Capital | 128.36 | 0.620 |
| 45 | 09015.1 | Kreaman Creek, Trib. To Salt Creek | Capital | 127.13 | 0.614 |
| 46 | 09005 | Sekiu Mainstem (RM 2-5) LWD Restoration | Capital | 122.16 | 0.590 |
| 47 | 09021 | Valley Creek Restoration Phase 3 | Capital | 118.39 | 0.572 |
| 48 | 19101 | Fish Passage Corrections on Joyce-Piedmont Road | Capital | 115.17 | 0.556 |
| 49 | 09004 | Hoko River/ Hermans Creek – Instream LWD Supplementation | Capital | 104.81 | 0.506 |
| 50 | 09018 | Elwha River Estuary Restoration | Capital | 102.19 | 0.494 |
Projects ranked 45 & up are eligible to apply for SRFB/PSAR funding
2022 & 2023 NOPLE Four Year Workplan Scatterplot
4-Yr Workplan Normalized Scores vs. Rank

Projects ranked 45 & up are eligible to apply for SRFB/PSAR funding.
| Rank | Normalized Score |
|---|---|
| 1 | 0.910 |
| 2 | 0.877 |
| 3 | 0.857 |
| 4 | 0.848 |
| 5 | 0.845 |
| 6 | 0.843 |
| 7 | 0.836 |
| 8 | 0.836 |
| 9 | 0.825 |
| 10 | 0.818 |
| 11 | 0.816 |
| 12 | 0.813 |
| 13 | 0.810 |
| 14 | 0.809 |
| 15 | 0.802 |
| 16 | 0.801 |
| 17 | 0.790 |
| 18 | 0.783 |
| 19 | 0.780 |
| 20 | 0.773 |
| 21 | 0.768 |
| 22 | 0.759 |
| 23 | 0.757 |
| 26 | 0.740 |
| 27 | 0.739 |
| 28 | 0.739 |
| 29 | 0.736 |
| 30 | 0.735 |
| 31 | 0.726 |
| 32 | 0.724 |
| 33 | 0.721 |
| 34 | 0.717 |
| 35 | 0.709 |
| 36 | 0.701 |
| 37 | 0.689 |
| 38 | 0.686 |
| 39 | 0.668 |
| 40 | 0.659 |
| 41 | 0.658 |
| 42 | 0.646 |
| 43 | 0.645 |
| 44 | 0.620 |
| 45 | 0.614 |
| 46 | 0.590 |
| 47 | 0.572 |
| 48 | 0.556 |
| 49 | 0.506 |
| 50 | 0.494 |
Assessment of 7 Additional Work Plan Projects
CoV = Coefficient of Variation (Standard deviation/Mean as %)
| ID | Title | Scorer(s) Outside 2 Std Deviations? | CoV% Flags for Specific Criteria? |
|---|---|---|---|
| 21001* | Expansion of Shipwreck Point NRCA | 0 | Yes (Criteria 5 & 8) |
| 19103.1 | Johnson Creek Triple Culverts Replacement | 0 | Yes (Criteria 5 & 7) |
| 09001.2 | Little Hoko River Large Wood Restoration | 0 | Yes (Criteria 5 & 7) |
| 10080.3 | Lyre River Protection and Restoration | 0 | Yes (Criterion 5) |
| 11088.2 | Ennis Creek Barrier Replacement | 2 | Yes (Criterion 7) |
| 09027.2 | Siebert Creek Ecosystem Protection & Restoration | 0 | Yes (Criteria 5 & 8) |
| 12098.1 | Dungeness River Instream Flow Restoration-Storage | 1 | Yes (Criteria 7, 8 & 12) |
Takeaways:
- 1 of 7 projects had 2 scorers who scored the project outside 2 standard deviations from the mean.
- 1 of 7 projects had 1 scorer who scored the project outside 2 standard deviations from the mean.
- 5 of 7 projects had a CoV% >50% for two or more criteria.
- Criterion 5: “Addresses an ESA-listed stock” was flagged for 5 projects.
- Criterion 7: “Protects high-quality fish habitat” was flagged for 4 projects.
- Criterion 8: “Restores formerly productive habitat” was flagged for 3 projects
- Criterion 12: “Project Readiness” was flagged for 1 project.
Individual Project Scoring
Expansion of Shipwreck Point NRCA (21001)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 2.96 | 13.74 | 0.0% | |
| 2 | Addresses limiting factor(s) | 2.00 | 2.50 | 2.00 | 3.00 | 5.00 | NS | 2.00 | 3.00 | 2.00 | 3.00 | 5.00 | 5.00 | 4.50 | 3.00 | 3.00 | 3.00 | 2.00 | 3.13 | 4.08 | 12.75 | 36.3% |
| 3 | Addresses stock status and trends | 4.00 | 2.50 | 2.00 | 5.00 | 4.00 | NS | 1.00 | 4.00 | 2.50 | 2.00 | 5.00 | 5.00 | 3.50 | 2.00 | 3.00 | 3.00 | 2.00 | 3.16 | 2.88 | 9.09 | 39.5% |
| 4 | Addresses progress toward recovery | 1.50 | 2.00 | 4.00 | 4.00 | 5.00 | NS | 1.00 | 4.00 | 2.00 | 4.00 | 5.00 | 4.50 | 3.00 | 2.00 | 3.00 | 4.00 | 2.00 | 3.19 | 2.81 | 8.96 | 40.5% |
| 5 | Addresses an ESA-listed stock | 3.00 | 2.00 | 2.00 | 4.00 | 3.50 | NS | 1.00 | 4.00 | 2.00 | 0.00 | 5.00 | 3.00 | 2.00 | 0.50 | 2.00 | 3.00 | 1.00 | 2.38 | 3.65 | 8.67 | 57.8% |
| 6 | Addresses other stocks | 4.00 | 3.00 | 5.00 | 3.50 | 5.00 | NS | 1.00 | 4.00 | 2.00 | 3.00 | 5.00 | 5.00 | 4.00 | 0.00 | 3.00 | 3.00 | 1.00 | 3.22 | 3.27 | 10.53 | 48.5% |
| 7 | Protects high-quality fish habitat | 3.00 | 2.00 | 4.00 | 5.00 | 4.50 | NS | 2.00 | 4.00 | 1.00 | 3.00 | 5.00 | 5.00 | 5.00 | 0.00 | 3.00 | 5.00 | 3.00 | 3.41 | 4.12 | 14.03 | 45.9% |
| 8 | Restores formerly productive habitat | 2.00 | 2.00 | 2.00 | 0.00 | 3.00 | NS | 1.50 | 2.00 | 1.00 | 2.00 | 3.00 | 3.00 | 0.00 | 2.00 | 0.00 | 0.00 | 3.00 | 1.66 | 4.04 | 6.69 | 68.6% |
| 9 | Supports restoration and maintenance of ecosystem functions | 3.00 | 2.00 | 5.00 | 3.00 | 5.00 | NS | 1.50 | 4.00 | 3.50 | 3.00 | 5.00 | 5.00 | 4.00 | 4.00 | 3.00 | 5.00 | 4.00 | 3.75 | 3.88 | 14.55 | 29.6% |
| 10 Spatial Scale of Influence | 2.50 | 2.50 | 3.50 | 3.50 | 4.50 | NS | 2.00 | 3.00 | 1.00 | 3.00 | 4.50 | 3.50 | 5.00 | 4.00 | 3.00 | 2.00 | 3.00 | 3.16 | 3.62 | 11.43 | 33.1% | |
| 11 | Temporal Scale of Influence | 5.00 | 3.00 | 5.00 | 5.00 | 5.00 | NS | 5.00 | 4.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 4.81 | 3.23 | 15.54 | 11.3% |
| 12 Project Readiness | 3.00 | 2.50 | 4.50 | 3.50 | 2.50 | NS | 2.00 | 2.00 | 1.00 | 3.00 | 3.00 | 5.00 | 0.00 | 1.00 | 4.00 | 3.00 | 3.00 | 2.69 | 2.85 | 7.66 | 48.5% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 3.14 | 2.55 | 3.64 | 3.68 | 4.30 | 2.05 | 3.55 | 2.30 | 2.97 | 4.59 | 4.47 | 3.39 | 2.34 | 3.05 | 3.39 | 2.80 | |
| CoV | 34.6% | 29.6% | 35.5% | 37.5% | 20.2% | #DIV/0! | 66.4% | 24.0% | 60.5% | 43.9% | 16.6% | 18.2% | 53.7% | 75.8% | 41.5% | 43.5% | 45.9% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N |
Comments
- Acquisition and protection of nearshore habitats as migration corridors is critical to the future success of many upland restoration projects throughout the Straits and Puget Sound
- What a great opportunity to protect mostly intact habitat and expand the only NRCA along the marine shoreline!
- The narrative lacks a clear stock status and trends, a clear definitive statement of stocks documented that use this estuary. Unclear if the project will restore formerly productive habitat because there is no information on stock trends/status. The projects lacks a clear goal on potential acquisition for the amount being asked. What are your priority parcels? Not quite clear what the end result would be. The narrative indicated that not much restoration was needed but points to turbidity from logging roads, will that turbidity remain or will it go away with acquisition. How will the logging road be restored or will it be decommissioned. I like that the project would expand on existing protected property.
- Criteria 3: scored 3.5 because it addresses a critical stock (nearshore Chinook) as per the stock status and trends table (which would rank this as a 5), however it addresses this stock in a more presumptive and indirect way, whereas the scoring criteria seems intended for projects that directly address those stock. Criteria 5 based on support of ESA fish use in the nearshore indirectly but with a large anticipated cumulative benefit.
- I’d like to better understand how the Watershed Priority scores were assigned to the Shipwreck Point, Lyre River, and Siebert Creek projects, and why all qualified as Nearshore. The Shipwreck Point and Lyre River projects seem to include nearshore aspects, but the Siebert Creek project appears to be confined to the stream itself. That being said, it would seem that the assigned Watershed Priority score would better reflect that that appears within the Watershed Priorities tab, or 1.867. By what criteria is the Nearshore Watershed Priority assigned?
- This looks like a great project, but its fit to salmon restoration and recovery is not strong. Think it would be better suited to other sources of funding.
Johnson Creek Triple Culverts Replacement (19103.1)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 2.96 | 10.35 | 0.0% | |
| 2 | Addresses limiting factor(s) | 4.00 | 3.00 | 5.00 | NS | 5.00 | 4.50 | 3.50 | 3.00 | 2.50 | 5.00 | 3.00 | NS | 4.50 | 4.00 | 2.00 | 4.00 | 4.00 | 3.80 | 4.08 | 15.50 | 24.8% |
| 3 | Addresses stock status and trends | 2.50 | 3.00 | 4.00 | NS | 4.00 | 4.00 | 4.00 | 3.00 | 3.50 | 5.00 | 4.00 | NS | 4.00 | 4.50 | 4.00 | 4.00 | 4.00 | 3.83 | 2.88 | 11.04 | 16.1% |
| 4 | Addresses progress toward recovery | 3.00 | 3.50 | 4.00 | NS | 5.00 | 4.00 | 2.00 | 3.00 | 4.00 | 3.00 | 5.00 | NS | 3.50 | 4.00 | 3.00 | 5.00 | 3.50 | 3.70 | 2.81 | 10.40 | 23.3% |
| 5 | Addresses an ESA-listed stock | 2.00 | 0.00 | 2.00 | NS | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | NS | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.27 | 3.65 | 0.97 | 263.9% |
| 6 | Addresses other stocks | 4.00 | 4.00 | 5.00 | NS | 5.00 | 3.50 | 2.00 | 3.00 | 3.50 | 5.00 | 5.00 | NS | 4.00 | 4.50 | 3.00 | 5.00 | 4.00 | 4.03 | 3.27 | 13.19 | 22.7% |
| 7 | Protects high-quality fish habitat | 4.50 | 3.50 | 4.00 | NS | 1.50 | 0.00 | 0.50 | 0.00 | 2.00 | 4.50 | 3.00 | NS | 0.00 | 0.00 | 0.00 | 0.00 | 2.00 | 1.70 | 4.12 | 7.00 | 105.3% |
| 8 | Restores formerly productive habitat | 3.00 | 4.00 | 5.00 | NS | 3.00 | 3.50 | 4.00 | 3.00 | 3.00 | 4.00 | 4.00 | NS | 3.50 | 4.00 | 2.50 | 5.00 | 3.50 | 3.67 | 4.04 | 14.81 | 19.7% |
| 9 | Supports restoration and maintenance of ecosystem functions | 4.00 | 4.50 | 5.00 | NS | 3.00 | 4.00 | 4.00 | 3.00 | 4.00 | 5.00 | 4.00 | NS | 4.50 | 4.00 | 2.00 | 5.00 | 3.50 | 3.97 | 3.88 | 15.39 | 21.0% |
| 10 Spatial Scale of Influence | 3.00 | 3.50 | 3.50 | NS | 2.50 | 3.50 | 3.00 | 2.00 | 3.00 | 4.00 | 4.00 | NS | 4.00 | 3.50 | 2.50 | 4.00 | 3.00 | 3.27 | 3.62 | 11.83 | 19.1% | |
| 11 | Temporal Scale of Influence | 4.50 | 4.00 | 4.50 | NS | 3.00 | 4.00 | 5.00 | 3.00 | 4.00 | 5.00 | 4.00 | NS | 5.00 | 5.00 | 4.00 | 5.00 | 5.00 | 4.33 | 3.23 | 14.00 | 16.1% |
| 12 Project Readiness | 4.00 | 4.00 | 5.00 | NS | 5.00 | 2.50 | 4.50 | 3.00 | 4.50 | 5.00 | 3.50 | NS | 3.00 | 4.50 | 4.50 | 5.00 | 4.00 | 4.13 | 2.85 | 11.78 | 19.6% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 3.50 | 3.37 | 4.21 | 3.37 | 3.08 | 3.00 | 2.46 | 3.12 | 4.08 | 3.58 | 3.29 | 3.46 | 2.58 | 3.79 | 3.33 | ||
| CoV | 22.8% | 34.1% | 21.8% | #DIV/0! | 46.5% | 49.3% | 52.2% | 48.6% | 38.7% | 35.7% | 36.1% | #DIV/0! | 49.5% | 48.3% | 55.9% | 48.9% | 38.0% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N |
Comments
- Improved access to wetlands and over wintering habitat will assist in run restoration for years to come. The complexity of the wetland habitat makes it worthwhile to increase salmonid access. As much of the burden as possible should fall on the road construction budget.
- I think this point has been hammered pretty hard already, but it really seems like the county should be putting up some money to deal with their poorly designed and unsustainable road. Maybe it takes another decade for them to come around to that fact, but I think that is okay. It does seem like the project holds real benefit for salmon though.
- This project needs to happen and it would be great if the county pitched in on costs. That said getting the creek out of the ditch and establishing better connectivity to upstream habitats are a plus.
Little Hoko River Large Wood Restoration (09001.2)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 3.494 | 2.96 | 10.35 | 0.0% | |
| 2 | Addresses limiting factor(s) | 3.50 | 3.00 | 4.00 | 4.50 | 5.00 | 4.00 | 4.00 | 3.00 | 4.00 | 5.00 | 4.00 | NS | 4.00 | 4.50 | 4.00 | 5.00 | ns | 4.10 | 4.08 | 16.73 | 15.4% |
| 3 | Addresses stock status and trends | 4.00 | 3.00 | 4.00 | 4.00 | 4.00 | 4.00 | 4.00 | 3.00 | 4.00 | 4.00 | 4.00 | NS | 4.00 | 4.50 | 4.00 | 5.00 | ns | 3.97 | 2.88 | 11.42 | 12.1% |
| 4 | Addresses progress toward recovery | 3.50 | 3.00 | 4.00 | 3.50 | 5.00 | 4.00 | 2.00 | 4.00 | 4.00 | 4.00 | 5.00 | NS | 3.00 | 4.50 | 3.00 | 5.00 | ns | 3.83 | 2.81 | 10.77 | 22.4% |
| 5 | Addresses an ESA-listed stock | 3.00 | 0.00 | 2.00 | 0.00 | 1.50 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | NS | 0.00 | 0.00 | 0.00 | 0.00 | ns | 0.43 | 3.65 | 1.58 | 217.5% |
| 6 | Addresses other stocks | 4.00 | 4.00 | 5.00 | 4.00 | 5.00 | 3.00 | 4.00 | 4.00 | 4.00 | 5.00 | 5.00 | NS | 4.00 | 4.50 | 4.00 | 5.00 | ns | 4.30 | 3.27 | 14.06 | 13.8% |
| 7 | Protects high-quality fish habitat | 3.00 | 3.00 | 3.50 | 0.00 | 4.00 | 0.00 | 0.50 | 3.00 | 3.50 | 5.00 | 3.00 | NS | 0.00 | 1.00 | 0.00 | 0.00 | ns | 1.97 | 4.12 | 8.10 | 90.9% |
| 8 | Restores formerly productive habitat | 3.00 | 3.50 | 4.00 | 5.00 | 4.50 | 3.00 | 4.00 | 4.00 | 5.00 | 5.00 | 4.00 | NS | 3.00 | 4.00 | 3.00 | 4.00 | ns | 3.93 | 4.04 | 15.89 | 18.5% |
| 9 | Supports restoration and maintenance of ecosystem functions | 4.50 | 3.50 | 4.00 | 4.50 | 4.50 | 4.00 | 4.50 | 4.00 | 5.00 | 5.00 | 4.00 | NS | 4.50 | 4.00 | 2.00 | 5.00 | ns | 4.20 | 3.88 | 16.30 | 17.9% |
| 10 Spatial Scale of Influence | 3.00 | 3.00 | 3.00 | 3.50 | 4.00 | 3.50 | 4.00 | 3.00 | 3.50 | 4.00 | 4.50 | NS | 3.50 | 4.00 | 3.00 | 4.00 | ns | 3.57 | 3.62 | 12.91 | 13.9% | |
| 11 | Temporal Scale of Influence | 4.50 | 4.00 | 3.50 | 5.00 | 4.00 | 3.50 | 5.00 | 3.00 | 4.50 | 4.00 | 4.00 | NS | 4.00 | 5.00 | 2.50 | 5.00 | ns | 4.10 | 3.23 | 13.24 | 18.6% |
| 12 Project Readiness | 4.50 | 3.00 | 4.00 | 3.00 | 5.00 | 3.00 | 3.00 | 4.00 | 4.50 | 5.00 | 4.50 | NS | 4.00 | 3.00 | 4.00 | 5.00 | ns | 3.97 | 2.85 | 11.31 | 19.9% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 3.67 | 3.04 | 3.71 | 3.37 | 4.17 | 2.96 | 3.21 | 3.21 | 3.79 | 4.12 | 3.79 | 3.12 | 3.54 | 2.75 | 3.87 | ||
| CoV | 16.8% | 33.9% | 19.5% | 50.2% | 23.6% | 48.6% | 49.0% | 34.8% | 34.4% | 34.3% | 34.9% | #DIV/0! | 48.8% | 43.2% | 52.3% | 48.6% | #DIV/0! |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N |
Comments
- This experienced project manager will get the most out of this habitat.
- I struggle with the 0 I gave for question number 5 regarding addresses an ESA-listed stock. I was unsure how to assign a score for this. Also for temporal scale the way I am understanding is that using larger wood with root wads will see that the project holds out longer than using the smaller wood previously used?
Lyre River Protection & Restoration (10080.3)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 2.96 | 13.74 | 0.0% | |
| 2 | Addresses limiting factor(s) | 3.50 | 3.00 | 2.00 | 4.00 | 5.00 | NS | 3.50 | 3.00 | 2.00 | 5.00 | 5.00 | 5.00 | 4.00 | 4.50 | 4.00 | 4.00 | 2.00 | 3.72 | 4.08 | 15.17 | 29.0% |
| 3 | Addresses stock status and trends | 3.50 | 3.00 | 3.00 | 5.00 | 4.00 | NS | 4.00 | 3.00 | 3.50 | 4.00 | 4.50 | 4.50 | 4.00 | 4.00 | 4.00 | 4.00 | 2.00 | 3.75 | 2.88 | 10.80 | 19.5% |
| 4 | Addresses progress toward recovery | 4.00 | 3.00 | 4.00 | 4.50 | 5.00 | NS | 2.50 | 3.00 | 2.00 | 5.00 | 4.50 | 4.50 | 4.00 | 4.00 | 4.00 | 4.00 | 3.00 | 3.81 | 2.81 | 10.71 | 22.9% |
| 5 | Addresses an ESA-listed stock | 3.50 | 2.00 | 5.00 | 3.00 | 3.50 | NS | 0.50 | 0.00 | 1.00 | 3.00 | 2.00 | 3.00 | 1.00 | 0.00 | 2.50 | 0.00 | 1.00 | 1.94 | 3.65 | 7.07 | 77.6% |
| 6 | Addresses other stocks | 4.00 | 4.00 | 4.00 | 4.00 | 5.00 | NS | 3.00 | 3.00 | 3.00 | 5.00 | 5.00 | 5.00 | 4.00 | 4.00 | 4.00 | 4.00 | 3.00 | 4.00 | 3.27 | 13.08 | 18.3% |
| 7 | Protects high-quality fish habitat | 4.00 | 3.50 | 4.00 | 5.00 | 4.50 | NS | 4.00 | 3.00 | 2.00 | 4.00 | 5.00 | 5.00 | 4.50 | 3.50 | 5.00 | 5.00 | 4.00 | 4.13 | 4.12 | 17.00 | 20.5% |
| 8 | Restores formerly productive habitat | 3.00 | 3.00 | 3.50 | 3.50 | 5.00 | NS | 3.00 | 4.00 | 3.00 | 5.00 | 3.00 | 3.00 | 0.00 | 2.50 | 0.00 | 5.00 | 3.00 | 3.09 | 4.04 | 12.50 | 46.9% |
| 9 | Supports restoration and maintenance of ecosystem functions | 4.50 | 3.00 | 4.00 | 3.50 | 5.00 | NS | 3.00 | 4.00 | 2.00 | 5.00 | 5.00 | 5.00 | 4.50 | 4.50 | 4.50 | 5.00 | 4.00 | 4.16 | 3.88 | 16.13 | 21.4% |
| 10 Spatial Scale of Influence | 3.50 | 3.00 | 3.00 | 3.00 | 4.50 | NS | 3.00 | 3.00 | 3.00 | 4.00 | 5.00 | 4.00 | 3.00 | 4.00 | 4.00 | 4.00 | 3.50 | 3.59 | 3.62 | 13.01 | 17.8% | |
| 11 | Temporal Scale of Influence | 5.00 | 4.00 | 5.00 | 5.00 | 4.50 | NS | 5.00 | 4.00 | 4.50 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 4.81 | 3.23 | 15.54 | 7.5% |
| 12 Project Readiness | 3.00 | 3.00 | 4.50 | 2.50 | 2.50 | NS | 1.50 | 2.00 | 1.00 | 5.00 | 3.00 | 5.00 | 1.50 | 2.00 | 3.00 | 4.00 | 3.00 | 2.91 | 2.85 | 8.28 | 41.8% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 3.84 | 3.26 | 3.89 | 3.97 | 4.43 | 3.14 | 3.05 | 2.64 | 4.55 | 4.30 | 4.47 | 3.34 | 3.55 | 3.72 | 4.05 | 3.18 | |
| CoV | 16.4% | 20.9% | 23.0% | 22.0% | 17.3% | #DIV/0! | 40.2% | 39.1% | 45.2% | 14.4% | 24.1% | 16.9% | 48.5% | 39.8% | 37.1% | 33.6% | 36.2% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N |
Comments
- The Lyre River can and should be a more productive system; channelization is a major problem not easily overcome. Property acquisition is an important first step
- It’s really hard to score a project where the parcels are completely unknown. I felt forced to err on the side of “they won’t be that great for salmon populations”. I’d like to see this project identify specific parcels they think are beneficial to salmon and have some potential to come on the market.
- I’d like to better understand how the Watershed Priority scores were assigned to the Shipwreck Point, Lyre River, and Siebert Creek projects, and why all qualified as Nearshore. The Shipwreck Point and Lyre River projects seem to include nearshore aspects, but the Siebert Creek project appears to be confined to the stream itself. That being said, it would seem that the assigned Watershed Priority score would better reflect that that appears within the Watershed Priorities tab, or 1.867. By what criteria is the Nearshore Watershed Priority assigned?
- Project description makes it unclear what parcels are being targeted so it reads kind of open ended. Its going to be difficult to recover the Lyre unless the channelized mainstem is restored. This is the dominant limiting factor in my opinion. The Lyre is too warm to support bull trout and although the WDF stream catalogue says there are pink salmon, I have never seen one.
Ennis Creek Barrier Replacement (11088.2)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.530 | 2.96 | 7.49 | 0.0% | |
| 2 | Addresses limiting factor(s) | 5.00 | 3.00 | 4.00 | 4.00 | 4.50 | 4.50 | 5.00 | 3.00 | 3.50 | NS | 3.00 | 5.00 | 4.50 | 4.00 | 2.50 | 5.00 | 4.00 | 4.03 | 4.08 | 16.45 | 20.5% |
| 3 | Addresses stock status and trends | 4.00 | 3.00 | 4.00 | 4.00 | 4.00 | 4.00 | 4.00 | 4.00 | 3.50 | NS | 4.00 | 5.00 | 4.00 | 4.00 | 2.50 | 5.00 | 4.00 | 3.94 | 2.88 | 11.34 | 15.3% |
| 4 | Addresses progress toward recovery | 4.00 | 3.00 | 3.50 | 3.00 | 4.00 | 4.00 | 3.50 | 4.00 | 3.50 | NS | 5.00 | 4.50 | 4.00 | 3.00 | 3.00 | 5.00 | 4.00 | 3.81 | 2.81 | 10.71 | 17.2% |
| 5 | Addresses an ESA-listed stock | 5.00 | 3.50 | 5.00 | 4.00 | 3.50 | 4.50 | 4.50 | 4.00 | 3.00 | NS | 2.00 | 5.00 | 3.00 | 4.00 | 3.50 | 0.00 | 3.50 | 3.63 | 3.65 | 13.23 | 35.1% |
| 6 | Addresses other stocks | 4.50 | 3.50 | 4.00 | 4.00 | 4.00 | 3.50 | 4.50 | 4.00 | 3.50 | NS | 5.00 | 5.00 | 4.50 | 3.00 | 3.50 | 5.00 | 3.50 | 4.06 | 3.27 | 13.28 | 15.5% |
| 7 | Protects high-quality fish habitat | 4.00 | 3.00 | 4.00 | 0.00 | 1.50 | 0.00 | 0.50 | 0.00 | 2.50 | NS | 3.00 | 3.50 | 0.00 | 1.00 | 0.00 | 0.00 | 2.00 | 1.56 | 4.12 | 6.44 | 100.4% |
| 8 | Restores formerly productive habitat | 3.50 | 4.00 | 4.50 | 3.50 | 4.00 | 3.00 | 4.50 | 3.50 | 3.00 | NS | 4.00 | 5.00 | 4.50 | 4.00 | 0.00 | 5.00 | 4.50 | 3.78 | 4.04 | 15.28 | 31.3% |
| 9 | Supports restoration and maintenance of ecosystem functions | 3.50 | 3.50 | 4.50 | 4.00 | 4.00 | 2.50 | 3.00 | 4.00 | 3.00 | NS | 4.00 | 5.00 | 4.50 | 4.00 | 2.00 | 5.00 | 3.50 | 3.75 | 3.88 | 14.55 | 22.3% |
| 10 Spatial Scale of Influence | 3.50 | 3.50 | 2.50 | 3.00 | 3.00 | 3.50 | 2.50 | 3.00 | 2.50 | NS | 3.00 | 5.00 | 5.00 | 4.00 | 3.00 | 5.00 | 3.00 | 3.44 | 3.62 | 12.44 | 25.4% | |
| 11 | Temporal Scale of Influence | 4.50 | 4.50 | 3.50 | 5.00 | 3.50 | 4.50 | 5.00 | 4.00 | 4.50 | NS | 4.00 | 5.00 | 5.00 | 5.00 | 4.00 | 5.00 | 5.00 | 4.50 | 3.23 | 14.54 | 12.2% |
| 12 Project Readiness | 4.00 | 4.00 | 4.00 | 2.50 | 2.50 | 3.50 | 2.00 | 2.00 | 4.00 | NS | 3.00 | 4.00 | 2.00 | 2.50 | 3.00 | 5.00 | 4.00 | 3.25 | 2.85 | 9.26 | 28.6% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 4.00 | 3.42 | 3.84 | 3.29 | 3.42 | 3.34 | 3.46 | 3.17 | 3.25 | 3.54 | 4.54 | 3.63 | 3.42 | 2.46 | 3.96 | 3.63 | |
| CoV | 17.5% | 16.2% | 19.4% | 38.5% | 25.5% | 37.9% | 40.1% | 38.2% | 19.0% | #DIV/0! | 26.5% | 17.7% | 41.1% | 31.0% | 51.6% | 50.0% | 22.8% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | Y | N | N | Y | N | N |
Comments
- Ennis Creek deserves a chance to return to its once, much more productive self.
- Indicating the percent passability for the culverts can help in understanding the importance of barrier removal against the removal of the upstream barrier on 101. I found it on the WA State Fish Barrier GIS map (33% passable) but others might not have known of that resource.
Siebert Creek Ecosystem Protection & Restoration (09027.2)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 4.639 | 2.96 | 13.74 | 0.0% | |
| 2 | Addresses limiting factor(s) | 2.50 | 3.00 | 2.00 | 3.00 | 5.00 | 3.00 | 3.00 | 3.00 | 2.00 | 3.00 | 5.00 | 4.50 | 3.00 | 3.00 | 4.00 | 4.00 | 2.00 | 3.24 | 4.08 | 13.20 | 29.5% |
| 3 | Addresses stock status and trends | 3.00 | 3.00 | 2.00 | 3.50 | 4.00 | 4.50 | 3.50 | 3.00 | 3.00 | 3.00 | 4.00 | 4.50 | 2.50 | 2.00 | 4.00 | 4.00 | 2.00 | 3.26 | 2.88 | 9.40 | 25.5% |
| 4 | Addresses progress toward recovery | 3.00 | 2.50 | 3.50 | 3.50 | 4.00 | 3.50 | 1.50 | 3.00 | 2.50 | 4.00 | 5.00 | 5.00 | 3.00 | 2.00 | 4.00 | 4.00 | 3.50 | 3.38 | 2.81 | 9.50 | 27.9% |
| 5 | Addresses an ESA-listed stock | 3.00 | 2.50 | 5.00 | 1.50 | 4.00 | 4.00 | 0.00 | 3.00 | 2.50 | 3.00 | 2.00 | 4.00 | 1.00 | 0.50 | 4.50 | 0.00 | 3.50 | 2.59 | 3.65 | 9.45 | 60.0% |
| 6 | Addresses other stocks | 3.00 | 3.00 | 3.50 | 3.50 | 4.00 | 3.50 | 3.00 | 3.00 | 2.50 | 3.00 | 5.00 | 5.00 | 4.00 | 0.00 | 4.00 | 4.00 | 3.50 | 3.38 | 3.27 | 11.06 | 32.9% |
| 7 | Protects high-quality fish habitat | 3.00 | 3.00 | 4.50 | 5.00 | 5.00 | 4.50 | 2.50 | 3.00 | 3.00 | 4.00 | 4.50 | 5.00 | 4.50 | 3.50 | 5.00 | 5.00 | 4.00 | 4.06 | 4.12 | 16.72 | 21.7% |
| 8 | Restores formerly productive habitat | 3.00 | 2.00 | 3.00 | 0.00 | 3.00 | 2.50 | 1.50 | 1.00 | 2.00 | 3.00 | 4.00 | 3.00 | 0.00 | 2.00 | 0.00 | 0.00 | 3.00 | 1.94 | 4.04 | 7.84 | 67.5% |
| 9 | Supports restoration and maintenance of ecosystem functions | 4.00 | 3.50 | 4.00 | 3.00 | 4.00 | 3.50 | 3.00 | 3.00 | 3.50 | 5.00 | 4.50 | 4.50 | 4.50 | 4.00 | 4.50 | 5.00 | 4.00 | 3.97 | 3.88 | 15.41 | 16.3% |
| 10 Spatial Scale of Influence | 3.00 | 3.50 | 2.50 | 3.50 | 4.00 | 4.00 | 1.00 | 3.00 | 2.00 | 4.00 | 5.00 | 4.00 | 3.00 | 3.00 | 4.00 | 4.00 | 3.00 | 3.32 | 3.62 | 12.03 | 28.1% | |
| 11 | Temporal Scale of Influence | 5.00 | 4.00 | 4.00 | 5.00 | 4.50 | 4.50 | 5.00 | 3.00 | 4.50 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 4.68 | 3.23 | 15.11 | 11.9% |
| 12 Project Readiness | 4.00 | 2.50 | 4.00 | 2.00 | 2.50 | 4.00 | 3.50 | 2.00 | 1.00 | 5.00 | 3.00 | 5.00 | 1.00 | 1.00 | 3.00 | 4.00 | 3.00 | 2.97 | 2.85 | 8.47 | 43.5% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 3.43 | 3.09 | 3.55 | 3.18 | 4.05 | 3.84 | 2.68 | 2.89 | 2.76 | 3.89 | 4.30 | 4.51 | 3.01 | 2.55 | 3.89 | 3.64 | 3.43 |
| CoV | 22.8% | 23.5% | 28.2% | 46.0% | 18.0% | 17.3% | 54.8% | 28.7% | 38.2% | 22.3% | 21.9% | 13.4% | 54.3% | 62.3% | 34.5% | 48.2% | 26.7% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N |
Comments
- This small creek has been surprisingly productive for steelhead and should be protected.
- The broadness of the proposal didn’t help me to gain a good understanding of how it directly benefits ESA-stocks in the nearshore though there was mention that it could extend to nearshore. The readiness of the project wasn’t mentioned, but I am assuming that as parcels become available and there was landowner willingness, they would be submitted for funding. Are there specific landowners that have expressed interest?
- When listing stock species the stock status and trends table indicates coho as dep/sta, a more detailed narrative of stocks and status would have been helpful. The narrative refers to other stocks but are not indicated in the stock status and trend table for Siebert creek. Having a definitive statement of known stock status rather than general statements may have resulted in different score. Question 8 ) Restores formerly productive habitat is not indicated in the narrative, there is no information on how productive historically this creek was or potential. Historical data would have been helpful and may have resulted in a different score.
- Criteria 5-Addresses ESA fish use in the nearshore indirectly
- I’d like to better understand how the Watershed Priority scores were assigned to the Shipwreck Point, Lyre River, and Siebert Creek projects, and why all qualified as Nearshore. The Shipwreck Point and Lyre River projects seem to include nearshore aspects, but the Siebert Creek project appears to be confined to the stream itself. That being said, it would seem that the assigned Watershed Priority score would better reflect that that appears within the Watershed Priorities tab, or 1.867. By what criteria is the Nearshore Watershed Priority assigned?
- Parcels were clearly identified in this proposal
Dungeness River Instream Flow Restoration- Storage (12098.1)
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 4.699 | 2.96 | 13.92 | 0.0% | |
| 2 | Addresses limiting factor(s) | 4.00 | 4.00 | 4.00 | 4.50 | 5.00 | 3.50 | 4.00 | 3.00 | 2.00 | NS | 5.00 | 5.00 | 5.00 | 4.00 | 1.00 | 5.00 | 2.00 | 3.81 | 4.08 | 15.56 | 32.4% |
| 3 | Addresses stock status and trends | 4.00 | 3.50 | 3.50 | 5.00 | 5.00 | 3.50 | 5.00 | 4.00 | 4.00 | NS | 5.00 | 5.00 | 5.00 | 4.00 | 1.00 | 5.00 | 3.00 | 4.09 | 2.88 | 11.79 | 26.5% |
| 4 | Addresses progress toward recovery | 4.00 | 4.00 | 4.00 | 4.50 | 5.00 | 3.50 | 4.00 | 4.00 | 2.00 | NS | 4.50 | 4.50 | 5.00 | 4.00 | 1.00 | 5.00 | 3.00 | 3.88 | 2.81 | 10.89 | 28.1% |
| 5 | Addresses an ESA-listed stock | 4.50 | 4.00 | 5.00 | 4.50 | 5.00 | 4.00 | 4.00 | 4.00 | 4.00 | NS | 5.00 | 5.00 | 5.00 | 4.50 | 2.50 | 5.00 | 2.50 | 4.28 | 3.65 | 15.63 | 19.1% |
| 6 | Addresses other stocks | 3.50 | 2.00 | 4.50 | 4.50 | 5.00 | 3.50 | 4.00 | 2.00 | 1.00 | NS | 5.00 | 5.00 | 5.00 | 2.00 | 1.00 | 5.00 | 3.00 | 3.50 | 3.27 | 11.45 | 42.4% |
| 7 | Protects high-quality fish habitat | 4.00 | 3.50 | 5.00 | 0.00 | 4.00 | 0.00 | 0.50 | 0.00 | 0.00 | NS | 3.00 | 4.00 | 4.00 | 2.50 | 0.00 | 0.00 | 1.00 | 1.97 | 4.12 | 8.11 | 97.9% |
| 8 | Restores formerly productive habitat | 4.00 | 3.50 | 4.00 | 3.00 | 5.00 | 3.50 | 3.00 | 3.00 | 2.00 | NS | 5.00 | 4.00 | 0.00 | 2.50 | 0.00 | 5.00 | 1.00 | 3.03 | 4.04 | 12.25 | 53.0% |
| 9 | Supports restoration and maintenance of ecosystem functions | 3.50 | 4.00 | 5.00 | 3.00 | 5.00 | 4.00 | 4.50 | 3.00 | 0.00 | NS | 5.00 | 5.00 | 4.50 | 4.50 | 2.00 | 5.00 | 1.00 | 3.69 | 3.88 | 14.31 | 41.7% |
| 10 Spatial Scale of Influence | 4.50 | 4.50 | 4.50 | 4.00 | 4.00 | 4.00 | 3.50 | 4.00 | 3.00 | NS | 5.00 | 5.00 | 5.00 | 4.00 | 2.00 | 5.00 | 4.00 | 4.13 | 3.62 | 14.93 | 19.5% | |
| 11 | Temporal Scale of Influence | 5.00 | 4.50 | 4.00 | 4.50 | 5.00 | 4.00 | 5.00 | 4.00 | 1.00 | NS | 5.00 | 5.00 | 5.00 | 5.00 | 3.00 | 5.00 | 2.50 | 4.22 | 3.23 | 13.63 | 27.4% |
| 12 Project Readiness | 4.00 | 2.50 | 4.50 | 2.50 | 4.00 | 1.00 | 1.00 | 2.00 | 0.50 | NS | 3.00 | 5.00 | 2.50 | 2.50 | 3.00 | 5.00 | 1.00 | 2.75 | 2.85 | 7.84 | 52.7% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 4.14 | 3.72 | 4.39 | 3.72 | 4.72 | 3.27 | 3.60 | 3.14 | 2.02 | 4.60 | 4.77 | 4.22 | 3.68 | 1.77 | 4.56 | 2.39 | |
| CoV | 10.9% | 21.5% | 11.2% | 38.0% | 9.4% | 41.6% | 40.4% | 41.4% | 79.9% | #DIV/0! | 16.6% | 8.2% | 36.0% | 27.8% | 78.0% | 31.5% | 51.9% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | Y | N | N |
Comments
- This is an extremely expensive project that should be funded by multiple sources. I just hope the project is large enough and the water cool enough to have a positive impact in a drought stricken fall.
- This project will also help the Dungeness River become more resilient to changing hydrology due to the effects of climate change.
- This is not a salmon restoration project and should not be funded with salmon recovery money.
Capital Project – MAXIMUM POSSIBLE SCORE
Date: 17-Dec-21
| ID | Criteria for Ranking | Score 0 to 5 with 5 being best | Mean Score | Weight | Weighted Mean Score | CoV (%) | ||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 | ||||||
| 1 Watershed Priority | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 5.000 | 2.96 | 14.81 | 0.0% | |
| 2 | Addresses limiting factor(s) | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 4.08 | 20.40 | 0.0% |
| 3 | Addresses stock status and trends | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 2.88 | 14.40 | 0.0% |
| 4 | Addresses progress toward recovery | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 2.81 | 14.05 | 0.0% |
| 5 | Addresses an ESA-listed stock | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 3.65 | 18.25 | 0.0% |
| 6 | Addresses other stocks | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 3.27 | 16.35 | 0.0% |
| 7 | Protects high-quality fish habitat | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 4.12 | 20.60 | 0.0% |
| 8 | Restores formerly productive habitat | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 4.04 | 20.20 | 0.0% |
| 9 | Supports restoration and maintenance of ecosystem functions | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 3.88 | 19.40 | 0.0% |
| 10 Spatial Scale of Influence | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 3.62 | 18.10 | 0.0% | |
| 11 | Temporal Scale of Influence | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 3.23 | 16.15 | 0.0% |
| 12 Project Readiness | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 2.85 | 14.25 | 0.0% | |
| Measure | Scorer 1 | Scorer 2 | Scorer 3 | Scorer 4 | Scorer 5 | Scorer 6 | Scorer 7 | Scorer 8 | Scorer 9 | Scorer 10 | Scorer 11 | Scorer 12 | Scorer 13 | Scorer 14 | Scorer 15 | Scorer 16 | Scorer 17 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Mean | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 | 5.00 |
| CoV | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% | 0.0% |
| Outside 2 Standard Deviations? | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N | N |
Final Watershed Priorities Sorted by Standardized Score
Date: 17-Dec-21
| WRIA | System | Overall Standardized Score (Max 5) |
|---|---|---|
| 18 Elwha River | 5.000 | |
| 18 Dungeness River | 4.699 | |
| 17 + 18 + 19 Nearshore | 4.639 | |
| 18 Morse Creek | 4.096 | |
| 19 Pysht River | 3.494 | |
| 19 Hoko River | 3.494 | |
| 19 Lyre River | 3.193 | |
| 19 Clallam River | 2.861 | |
| 19 Sekiu River | 2.831 | |
| 19 Sail River | 2.530 | |
| 18 Ennis Creek | 2.530 | |
| 19 Salt Creek | 2.530 | |
| 19 Deep Creek | 2.199 | |
| 19 Colville Creek | 1.898 | |
| 17 Jimmycomelately Creek | 1.867 | |
| 19 East Twin River | 1.867 | |
| 19 West Twin River | 1.867 | |
| 18 McDonald Creek | 1.867 | |
| 18 Siebert Creek | 1.867 | |
| 17 Chicken Coop Creek | 1.566 | |
| 17 Dean Creek | 1.566 | |
| 17 Johnson Creek | 1.566 | |
| 19 Butler Creek (19.0112) | 1.566 | |
| 19 Field Creek | 1.566 | |
| 19 Jim Creek | 1.566 | |
| 19 Joe Creek | 1.566 | |
| 19 Murdock Creek | 1.566 | |
| 18 Peabody Creek | 1.566 | |
| 18 Lees Creek | 1.566 | |
| 18 Meadowbrook Creek | 1.566 | |
| 18 Tumwater Creek | 1.566 | |
| 18 Valley Creek | 1.566 | |
| 18 Bell Creek | 0.904 | |
| 18 Cooper Creek (18.0017) | 0.904 | |
| 18 Cassalery Creek | 0.904 | |
| 19 Olsen Creek | 0.904 | |
| 18 Bagley Creek | 0.904 | |
| 18 Dry Creek | 0.904 | |
| 18 Gierin Creek | 0.904 |
2022 & 2023 NOPLE Four Year Workplan – Capital Projects Criteria
Date: 17-Dec-21
| ID | Criteria for Ranking | Criteria Narrative | 0 | 1 | 2 | 3 | 4 | 5 | Mean Weight |
|---|---|---|---|---|---|---|---|---|---|
| 1 | Watershed Priority | What is the watershed priority score for this proposal? This criterion is mandated by regulation. The score is calculated based on data concerning historical and current productivity and stock diversity of the NOPLE watersheds. This score is added by Lead Entity staff for the watershed(s) covered by the proposed project. | Watershed priority scores have been calculated for each NOPLE watershed. The calculation produced a numerical score based on difference between historical and current watershed productivity plus historical number of stock and stock elements. See separate Watershed Priority Table for data and more details on the calculation. | 2.96 | |||||
| 2 | Addresses limiting factor(s) | How well does the proposed work address the limiting factor(s) pertinent to the watershed and stock? | Does not mention or address a limiting factor at all | Mentions a limiting factor, but addresses only vaguely | Indirectly addresses a limiting factor but only minimally | Indirectly addresses a limiting factor, but only moderately, OR Directly addresses limiting factor, but only minimally | Addresses a limiting factor directly and moderately | Addresses a limiting factor directly and substantially | 4.08 |
| 3 | Addresses stock status and trends | How well does the proposed work address the status and trends of the stock(s) of interest? | Stock fully recovered; no more work needed | Addresses recovered stock | Addresses rebuilding stock | Addresses depressed stock that is increasing | Addresses depressed stock that is decreasing | Addresses critical stock | 2.88 |
| 4 | Addresses progress toward recovery | To what extent does the watershed or nearshore area need further habitat protection and/or restoration efforts? | Recovery completed; needs no further efforts to complete recovery | Recovery in progress; needs just a little protection and/or restoration effort to complete recovery | Recovery in progress; needs some protection and/or restoration effort to complete recovery | Recovery in progress; needs moderate protection and/or restoration effort to complete recovery | Recovery in progress; needs more than moderate protection and/or restoration effort to complete recovery | Recovery in progress; needs substantial or major protection and/or restoration effort to complete recovery | 2.81 |
| 5 | Addresses an ESA- listed stock | To what extent does the project benefit listed stocks? | Does not mention or address a listed stock at all | Mentions listed stock, but addresses only vaguely | Indirectly addresses listed stock and only minimally | Indirectly addresses listed stock moderately OR Directly addresses listed stock only minimally | Directly and moderately addresses listed stock | Directly and substantially addresses listed stock | 3.65 |
| 6 | Addresses other stocks | To what extent does the project benefit non-listed stocks? | Does not mention or address a non-listed stock at all | Mentions non-listed stock, but addresses only vaguely | Indirectly addresses non-listed stock and only minimally | Indirectly addresses non-listed stock moderately OR Directly addresses non-listed stock only minimally | Directly and moderately addresses non-listed stock | Directly and substantially addresses non-listed stock | 3.27 |
| 7 | Protects high- quality fish habitat | How well does the proposed work and instrument protect fish habitat? | Does not mention or address criterion at all; benefits not discernible | Mentions habitat protections but addresses criterion only vaguely; benefits uncertain at best | Addresses criterion only indirectly with only minimal benefits | Addresses criterion indirectly with moderate benefits OR addresses criterion directly with only minimal benefits | Addresses criterion directly with moderate benefits | Addresses criterion directly with substantial benefits | 4.12 |
| 8 | Restores formerly productive habitat | How well does the project restore formerly productive habitat? | Does not mention or address criterion at all; benefits not discernible | Mentions habitat restoration but addresses criterion only vaguely; benefits uncertain at best | Addresses criterion only indirectly with only minimal benefits | Addresses criterion indirectly with moderate benefits OR addresses criterion directly with only minimal benefits | Addresses criterion directly with moderate benefits | Addresses criterion directly with substantial benefits | 4.04 |
| 9 | Supports restoration and maintenance of ecosystem functions | How well does the project restore and maintain ecosystem functions? | Does not mention or address criterion at all; benefits not discernible | Mentions ecosystem restoration but addresses criterion only vaguely; benefits uncertain at best | Addresses criterion only indirectly with only minimal benefits | Addresses criterion indirectly with moderate benefits OR addresses criterion directly with only minimal benefits | Addresses criterion directly with moderate benefits | Addresses criterion directly with substantial benefits | 3.88 |
| 10 | Spatial Scale of Influence | How far does the spatial scale of influence extend through a watershed or nearshore area? | Potential spatial scale of influence not mentioned or addressed; scale of benefits not discernible | Potential scale of influence minimal; Benefits local (limited to project area) at most and uncertain | Potential scale of influence slight; scale of benefits more than local and discernible | Potential scale of influence over a moderate portion of a watershed or nearshore area; benefits moderate and spread beyond the project area through part of the system | Potential scale of influence over a majority of a watershed or nearshore area; benefits more than moderate and spread through much of the system | Potential scale of influence over a watershed or nearshore area; benefits substantial and spread through essentially all of the system | 3.62 |
| 11 | Temporal Scale of Influence | How far does the temporal scale of influence extend through a watershed or nearshore area? | Potential temporal scale of influence not mentioned or addressed; scale of benefits not discernible | Potential scale of influence minimal; Benefits seasonal at most and uncertain | Potential scale of influence slight; scale of benefits more than seasonal but less than 1 year and discernible | Potential scale of influence of moderate duration; benefits moderate and endure for 2 to 4 years | Potential scale of influence of more than moderate duration; benefits moderate and endure for 5 to 10 years | Potential scale of influence of long- term to indefinite duration; benefits substantial and endure beyond 10 years | 3.23 |
| 12 | Project Readiness | How ready is the project to start now, if funded? | Not ready for foreseeable future; Time to overcome known obstacles and fulfill requirements is not determined but not in immediate future | Not ready for some years; time to overcome known obstacles and fulfill requirements is greater than 5 years | Ready within 3 or 4 years; Remaining obstacles and requirements can be resolved over 3 to 4 years | Ready within 2 years; remaining obstacles and requirements can be resolved within 2 years | Ready next year; remaining obstacles and requirements can be resolved within 1 year | Ready to start now given award of funds; no remaining obstacles or requirements; a ready-to-go project | 2.85 |
Capital Projects Criteria Sorted by Mean Weight
Date: 17-Dec-21
| ID | Criteria for Ranking | Criteria Narrative | 0 | 1 | 2 | 3 | 4 | 5 | Mean Weight |
|---|---|---|---|---|---|---|---|---|---|
| 7 | Protects high- quality fish habitat | How well does the proposed work and instrument protect fish habitat? | Does not mention or address criterion at all; benefits not discernible | Mentions habitat protections but addresses criterion only vaguely; benefits uncertain at best | Addresses criterion only indirectly with only minimal benefits | Addresses criterion indirectly with moderate benefits OR addresses criterion directly with only minimal benefits | Addresses criterion directly with moderate benefits | Addresses criterion directly with substantial benefits | 4.12 |
| 2 | Addresses limiting factor(s) | How well does the proposed work address the limiting factor(s) pertinent to the watershed and stock? | Does not mention or address a limiting factor at all | Mentions a limiting factor, but addresses only vaguely | Indirectly addresses a limiting factor but only minimally | Indirectly addresses a limiting factor, but only moderately, OR Directly addresses limiting factor, but only minimally | Addresses a limiting factor directly and moderately | Addresses a limiting factor directly and substantially | 4.08 |
| 8 | Restores formerly productive habitat | How well does the project restore formerly productive habitat? | Does not mention or address criterion at all; benefits not discernible | Mentions habitat restoration but addresses criterion only vaguely; benefits uncertain at best | Addresses criterion only indirectly with only minimal benefits | Addresses criterion indirectly with moderate benefits OR addresses criterion directly with only minimal benefits | Addresses criterion directly with moderate benefits | Addresses criterion directly with substantial benefits | 4.04 |
| 9 | Supports restoration and maintenance of ecosystem functions | How well does the project restore and maintain ecosystem functions? | Does not mention or address criterion at all; benefits not discernible | Mentions ecosystem restoration but addresses criterion only vaguely; benefits uncertain at best | Addresses criterion only indirectly with only minimal benefits | Addresses criterion indirectly with moderate benefits OR addresses criterion directly with only minimal benefits | Addresses criterion directly with moderate benefits | Addresses criterion directly with substantial benefits | 3.88 |
| 5 | Addresses an ESA- listed stock | To what extent does the project benefit listed stocks? | Does not mention or address a listed stock at all | Mentions listed stock, but addresses only vaguely | Indirectly addresses listed stock and only minimally | Indirectly addresses listed stock moderately OR Directly addresses listed stock only minimally | Directly and moderately addresses listed stock | Directly and substantially addresses listed stock | 3.65 |
| 10 | Spatial Scale of Influence | How far does the spatial scale of influence extend through a watershed or nearshore area? | Potential spatial scale of influence not mentioned or addressed; scale of benefits not discernible | Potential scale of influence minimal; Benefits local (limited to project area) at most and uncertain | Potential scale of influence slight; scale of benefits more than local and discernible | Potential scale of influence over a moderate portion of a watershed or nearshore area; benefits moderate and spread beyond the project area through part of the system | Potential scale of influence over a majority of a watershed or nearshore area; benefits more than moderate and spread through much of the system | Potential scale of influence over a watershed or nearshore area; benefits substantial and spread through essentially all of the system | 3.62 |
| 6 | Addresses other stocks | To what extent does the project benefit non-listed stocks? | Does not mention or address a non-listed stock at all | Mentions non-listed stock, but addresses only vaguely | Indirectly addresses non-listed stock and only minimally | Indirectly addresses non-listed stock moderately OR Directly addresses non-listed stock only minimally | Directly and moderately addresses non-listed stock | Directly and substantially addresses non-listed stock | 3.27 |
| 11 | Temporal Scale of Influence | How far does the temporal scale of influence extend through a watershed or nearshore area? | Potential temporal scale of influence not mentioned or addressed; scale of benefits not discernible | Potential scale of influence minimal; Benefits seasonal at most and uncertain | Potential scale of influence slight; scale of benefits more than seasonal but less than 1 year and discernible | Potential scale of influence of moderate duration; benefits moderate and endure for 2 to 4 years | Potential scale of influence of more than moderate duration; benefits moderate and endure for 5 to 10 years | Potential scale of influence of long- term to indefinite duration; benefits substantial and endure beyond 10 years | 3.23 |
| 1 | Watershed Priority | What is the watershed priority score for this proposal? This criterion is mandated by regulation. The score is calculated based on data concerning historical and current productivity and stock diversity of the NOPLE watersheds. This score is added by Lead Entity staff for the watershed(s) covered by the proposed project. | Watershed priority scores have been calculated for each NOPLE watershed. The calculation produced a numerical score based on difference between historical and current watershed productivity plus historical number of stock and stock elements. See separate Watershed Priority Table for data and more details on the calculation. | 2.96 | |||||
| 3 | Addresses stock status and trends | How well does the proposed work address the status and trends of the stock(s) of interest? | Stock fully recovered; no more work needed | Addresses recovered stock | Addresses rebuilding stock | Addresses depressed stock that is increasing | Addresses depressed stock that is decreasing | Addresses critical stock | 2.88 |
| 12 | Project Readiness | How ready is the project to start now, if funded? | Not ready for foreseeable future; Time to overcome known obstacles and fulfill requirements is not determined but not in immediate future | Not ready for some years; time to overcome known obstacles and fulfill requirements is greater than 5 years | Ready within 3 or 4 years; Remaining obstacles and requirements can be resolved over 3 to 4 years | Ready within 2 years; remaining obstacles and requirements can be resolved within 2 years | Ready next year; remaining obstacles and requirements can be resolved within 1 year | Ready to start now given award of funds; no remaining obstacles or requirements; a ready-to-go project | 2.85 |
| 4 | Addresses progress toward recovery | To what extent does the watershed or nearshore area need further habitat protection and/or restoration efforts? | Recovery completed; needs no further efforts to complete recovery | Recovery in progress; needs just a little protection and/or restoration effort to complete recovery | Recovery in progress; needs some protection and/or restoration effort to complete recovery | Recovery in progress; needs moderate protection and/or restoration effort to complete recovery | Recovery in progress; needs more than moderate protection and/or restoration effort to complete recovery | Recovery in progress; needs substantial or major protection and/or restoration effort to complete recovery | 2.81 |
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