Species | Channel Gradient (%) (Naturally Accessible Waterbodies) | Channel Gradient (%) (Spawning Habitat) | Mean annual discharge (m3/s) (Spawning Habitat) | Channel Gradient (%) (Rearing Habitat) | Mean annual discharge (m3/s) (Rearing Habitat) | Minimum Lake area (ha) (Rearing Habitat) | Multiplier (1.5x) (Rearing Habitat) |
|---|---|---|---|---|---|---|---|
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 [9][13] | Wetland | |
Sockeye Salmon | 0-15 | 0-2 [14][15] | 0.175-65 [3][4][5][6] | 200 [5] | Lake | ||
Steelhead | 0-20 | 0-4 [2][16] | 0.447-75 [3][4][6] | 0-7.4 [8] | 0.02-60 [9][13] |
Data Download
Coming soon.
Connectivity Status Assessment Methods
The connectivity status assessment for anadromous salmonids in the Bulkley River watershed builds on existing connectivity modelling work undertaken by the BC 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 1. 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 | Notes | Supporting Links |
|---|---|---|---|---|---|---|---|
123375 | 1800131 | Tributary to Thompson Creek | Hihgway 16 | Stream crossing - CBS | Crossing is upstream of major tributary with limited flows and poor substrates/habitat quality lacking suitable rearing and spawning habitat. Farther upstream from farm is medium quality habitat but short habitat gain. | https://www.newgraphenvironment.com/fish_passage_skeena_2021_reporting/thompson-creek---198066-123377-123375---appendix.html |
Barrier Id | Modelled Crossing Id | Watercourse Name | Road Name | Structure Type | Reason For Exclusion | Method Of Exclusion | Reason | Notes | Supporting Links |
|---|---|---|---|---|---|---|---|---|---|
1001800752 | 1800752 | Tributary to Elwin Lake | Unnamed | Stream crossing - Ford | Passable | Imagery review | Ford visible on satellite imagery. Could not be reached in the field. | ||
123776 | 24703647 | Corya Creek | Highway 16 | Stream crossing - OBS | Passable | Field assessment | Bridge, fairly recent replacement | ||
197657 | 1800067 | Perow Creek | Highway 16 | Stream crossing - CBS | Passable | Field assessment | Fully backwatered, scores as passable | ||
197900 | 1805532 | Crow Creek | Railway | Stream crossing - OBS | Passable | Field assessment | Bridge | ||
197902 | Tributary to Bulkley River | Rose Lake Cutoff Road | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat, dry at time of assessment | very small channel (1.5 m width), no modeled key habitat upstream, likely due to low discharge values. | ||
197903 | 1800180 | Tributary to Bulkley River | Rose Lake Cutoff Road | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat, dry at time of assessment | very small channel (1.5 m width), no modeled key habitat upstream, likely due to low discharge values. | |
197904 | 1800372 | Tributary to Bulkley River | Crow Creek Road | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat, dry with dredged channel at time of assessment | No modeled key habitat upstream | |
197905 | 1803682 | Crow Creek | Maxan Creek FSR | Stream crossing - OBS | Passable | Field assessment | Bridge | ||
197906 | 1803706 | Tributary to Maxan Creek | Maxan Creek FSR | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat, small channel, dry at time of assessment | No modeled key habitat upstream | |
197908 | 1803697 | Tributary to Maxan Creek | Maxan Creek FSR | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat, very small channel, dry at time of assessment | No modeled key habitat upstream | |
197910 | 1804694 | Trib to Maxan Lake | Spur 30 | Stream crossing - OBS | Passable | Field assessment | Bridge | ||
197913 | 1802088 | Robert Hatch Creek | Unnamed | Stream crossing - Ford | Passable | Field assessment | Ford. No passage issues but intense cattle-related impacts. | ||
197914 | 1802089 | Johnny David Creek | Unnamed | Stream crossing - Ford | Passable | Field assessment | Ford. No passage issues but intense cattle-related impacts. | ||
197955 | 1800422 | Ailport Creek | Transmission line | Stream crossing - Ford | Passable | Field assessment | Ford | ||
197956 | 1801133 | Tributary to Bulkley River | Spur | Stream crossing - Ford | Passable | Field assessment | No crossing present at this location. Private land access. | ||
197957 | 1801969 | Tributary to Bulkley River | Spur | Stream crossing - OBS | Passable | Field assessment | ATV bridge over historic culverts that have been washed out. No fish passage issues. | ||
197963 | 1805531 | Tributary to Bulkley River | Railway | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat, no modeled key habitat upstream. | Beavers have clogged both inlets (double barrel). Significant sized marsh ~40m upstream with beaver dam 1.5 - 2m high on outlet of wetland. | |
197964 | 1805529 | Bulkley River | Railway | Stream crossing - CBS | Passable | Field assessment | Embedded and backwatered structure. Not likely causing any fish passage issues. Wetland-type area. | ||
197969 | 1800583 | Bulkley River | Raymond Road | Stream crossing - OBS | Passable | Field assessment | Bridge | ||
197970 | 1803813 | Tributary to Broman Lake | Broman Lake FSR | Stream crossing - CBS | No key upstream habitat | Field assessment | Low quality habitat. Channel dry with small amount of water downstream. No modeled key habitat upstream | ||
197972 | 1802040 | Tributary to Broman Lake | Transmission line | Stream crossing - CBS | No key upstream habitat | Field assessment | Stream dry upstream and downstream except small outlet pool. No modeled key habitat upstream | ||
198041 | 1802760 | Deep Creek | Spur | Stream crossing - OBS | Passable | Field assessment | Bridge | ||
198042 | 1805553 | Glass Creek | Railway | Stream crossing - CBS | Passable | Field assessment | Likely closed-bottom structures (concrete boxes) but look like bridges. Deep channel with lake upstream. Not likely presenting much of barrier due to deep, slow flows. | ||
198047 | 1801773 | Boulder Creek | Unnamed | Stream crossing - Ford | Passable | Field assessment | Structure does not exist; road deactivated | ||
198109 | 1801071 | Perow Creek | Transmission line | Stream crossing - Ford | Passable | Field assessment | Ford | ||
198111 | 1802798 | Coffin Creek | Spur | Stream crossing - Ford | Passable | Field assessment | Ford. No signs of obstruction visible. | https://www.newgraphenvironment.com/fish_passage_bulkley_2022_reporting/appendix---phase-1-fish-passage-assessment-data-and-photos.html | |
198113 | 1802069 | Johnny David Creek | Spur | Stream crossing - Ford | Passable | Field assessment | Ford | Beaver dam in old road location. No obstructions noted. | |
1001802820 | Deep Creek | Unnamed | None | No structure | Field assessment | No structure. Private land access with permission from landowner. | |||
1001805665 | Canyon Creek | Private | None | No structure | Local knowledge | Adjacent landowner confirmed that crossing does not exist. | |||
1001802482 | Vallee Creek | Unnamed | None | No structure | Local knowledge | Landlord reports that there is no structure here. | |||
1001802044 | Ailport Creek | Unnamed | Stream crossing - OBS | Passable | Field assessment | Bridge on private land | |||
1001802374 | Causqua Creek | None | No structure | Field assessment | Structure does not exist |