Species | Channel Gradient (%)(Naturally Accessible Waterbodies) | Channel Gradient (%) | Mean annual discharge (m3/s) | Channel gradient (%) | Mean Annual discharge (m3/s) | Minimum Lake area (ha) | Multiplier (1.5x) |
|---|---|---|---|---|---|---|---|
Chinook Salmon | 0-15 | 0-3 [1] [2] | 0.46-322.5 [3][4][5][6][7] | 0-5 [5][8] | 0.28-100 [9] | ||
Coho Salmon | 0-15 | 0-5 [6][10] | 0.164-59.15 [3][4][5][10][11] | 0-5 [8][12] | 0.03-40 [8][13] | Wetland | |
Sockeye Salmon | 0-15 | 0-2 [14][15] | 0.175-65 [3][4][5][6] | 200 [5] | Lake |
Data Download
Coming soon
Connectivity Status Assessment Methods
The connectivity status assessment for anadromous salmonids in the Horsefly River watershed builds on existing connectivity modelling work undertaken by the B.C. Fish Passage Technical Working Group, resulting in a flexible, customizable open-source spatial model called “bcfishpass”. The model spatially locates known and modelled barriers to fish passage, identifies potential spawning and rearing habitat for focal species, and estimates the amount of habitat that is currently accessible to focal species. The model uses an adapted version of the Intrinsic Potential (IP) fish habitat modelling framework (see Sheer et al. (2009) for an overview of the IP framework). The habitat model uses two geomorphic characteristics of the stream network — channel gradient and mean annual discharge — to identify potential spawning habitat and rearing habitat for each focal species. The habitat model does not attempt to definitively map each habitat type nor estimate habitat quality, but rather identifies stream segments that have high potential to support spawning or rearing habitat for each species based on the geomorphic characteristics of the segment. For more details on the connectivity and habitat model structure and parameters, please see (Mazany-Wright et al. (2021a)). The variables and thresholds used to model potential spawning and rearing habitat for each focal species are summarized in Table 15. The quantity of modelled habitat for each species was aggregated for each habitat type and represents a linear measure of potential habitat. To recognize the rearing value provided by features represented by polygons for certain species (e.g., wetlands for Coho Salmon and lakes for Sockeye Salmon) a multiplier of 1.5x the length of the stream segments flowing through the polygons was applied.
References: [1] Busch et al. (2011). [2] Cooney and Holzer (2006). [3] Bjornn and Reiser (1991). [4] Neuman and Newcombe (1977). [5] Woll, Albert, and Whited (2017). [6] Roberge et al. (2002). [7] Raleigh and Miller (1986). [8] Porter et al. (2008). [9] Agrawal et al. (2005). [10] Sloat, Reeves, and Christiansen (2017). [11] McMahon (1983). [12] Rosenfeld, Porter, and Parkinson (2000). [13] Burnett et al. (2007). [14] Lake (1999). [15] Hoopes (1972).
Other Tables
Barrier Id | Modelled Crossing Id | Watercourse Name | Road Name | Structure Type | Reason For Exclusion | Method Of Exclusion | Reason | Notes | Supporting Links |
|---|---|---|---|---|---|---|---|---|---|
197761 | 6800240 | Trib to Horsefly River | unnamed | Stream crossing - Ford | Passable | Field assessment | Cattle trail/ford, location likely refers to historic crossing that has been decommissioned and abandoned at edge of channel | ||
198871 | 6800319 | Niquidet Creek | unnamed | Stream crossing - OBS | Passable | Field assessment | Pedestrian bridge across creek, not a barrier to fish passage | ||
57292 | 6802284 | Bassett Creek | 500 | Stream crossing - CBS | No key upstream habitat | Field assessment | Impassable natural barrier downstream | ||
57317 | 6800584 | Trib to McKinley Creek | R01350-524 | Stream crossing - CBS | No key upstream habitat | Field assessment | No suitable habitat: small defined channel but no water = poor spawning, rearing, overwintering potential. No modeled key habitat upstream. | ||
57596 | 6800587 | Bassett Creek | R14189-4C | None | No structure | Field assessment | No stream crossing identified but large woody debris jam present and passable to fish | ||
773d7d7c-11b7-4c8c-b761-ff1d4d60818a | Rat/Peter Creek | n/a | None | No structure | Field assessment | Dam confirmed to not exist (formerly structure 1100000814) | |||
1006800520 | Woodjam Creek | Private | None | No structure | Local knowledge | Access permission not granted. Landowners confirmed bridge/barrier no longer present | |||
1006801356 | Trib to Horsefly Lake | R01350 | None | No structure | Field assessment | Crossing does not exist | |||
a423c60a-dfb1-4414-bba3-bd57c89c6357 | Gibbons Creek | n/a | Dam | Passable | Field assessment | Dam appears to be off channel with water flowing around the dam, no fish passage issues (formerly structure 1100001822) | |||
197763 | Niquidet Creek | unnamed | Stream crossing - Ford | Passable | Field assessment | Location is a cattle trail/ford, not a barrier to fish | |||
40fc35b1-a834-4821-9c09-e8c64a646252 | Niquidet Creek | n/a | None | No structure | Field assessment | Dam confirmed to not exist (formerly structure 1100000763) | |||
17e18f43-e699-4e2c-ae73-e3f3e48de11f | Gibbons Creek | n/a | None | No structure | Field assessment | Dam confirmed to not exist (formerly structure 1100000243) | |||
198875 | Gibbons Creek | unnamed | Stream crossing - OBS | Passable | Field assessment | Road carried by a 2200 mm diameter OBS arch culvert that is 12 m long, does not represent a barrier to fish passage | |||
1006801130 | Wilmot Creek | unnamed | None | No structure | Field assessment | Crossing does not exist | |||
1006800484 | Molybdenite Creek | unnamed | None | No structure | Field assessment | Crossing does not exist | |||
198161 | Trib to Elbow Lake | unnamed | Stream crossing - OBS | Passable | Field assessment | Open bottom arch culvert | |||
1006800298 | Patenaude Creek | unnamed | None | No structure | Field assessment | Crossing does not exist |
Barrier Id | Modelled Crossing Id | Watercourse Name | Road Name | Structure Type | Structure Owner | Barrier Status | Partial Passability | Assessment Type Completed | Total Hab Gain Set | Num Barriers Set | Next Steps | Notes | Supporting Links |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1200000002 | Patenaude Creek | Private | Stream crossing - OBS | Private | BARRIER | Informal assessment | 3.62 | 1 | Barrier assessment (data deficient structures only) | Complete barrier assessment to verify status | |||
126438 | 6800525 | Trib to Horsefly River | Private | Stream crossing - CBS | Private | POTENTIAL | Barrier assessment | 0.85 | 1 | Engage with barrier owner | Can't access site (landowner refusal). Brian checking with local consultant if he knows anything about the crossing. Bring to regulator if no resolution. | http://a100.gov.bc.ca/pub/pscismap/imageViewer.do?habitatConfirmationId=1882 | |
1006800220 | 6800220 | Trib to Harpers Lake | unnamed | Other | Private | POTENTIAL | Other | 0.69 | 2 | Non-actionable | |||
57430 | 6801719 | Gifford Creek | Hendrix-McKinley | Stream crossing - CBS | FLNRO | BARRIER | Habitat confirmation | 0.02 | 1 | In-depth habitat investigation (data deficient structures only) | Coho present downstream, some steep sections to falls, salmonids throughout to falls | http://a100.gov.bc.ca/pub/pscismap/imageViewer.do?habitatConfirmationId=703 | |
124271 | MacLean Creek | Private | Stream crossing - CBS | Private | BARRIER | Habitat confirmation | Engage with barrier owner | Last assessed 2017. Can't access. Brian checking with local consultant on status of crossing. Bring in regulator if no resolution | http://a100.gov.bc.ca/pub/pscismap/imageViewer.do?habitatConfirmationId=681 |