August 11 Snorkel SCC side channel network (SBA, SCC3) feet 707
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1 Date Survey Type Habitat July 29 Snorkel (reconnaissance) Table 1. Fish use survey schedule 2004 Water temperature 1 (ºC) Estimated Mean visibility 2 discharge 3 (cfs) Mainstem (units #1 42) ND ND 814 August 5 Snorkel Mainstem (units #1 23) (MS#3, 23) feet 665 August 11 Snorkel SCC side channel network (SBA, SCC3) feet 707 August 12 Snorkel Mainstem (units #24A 48) (MS#48) feet 676 August 17 Snorkel SCB side channel network (SCB1) feet 595 September 6 Snorkel Mainstem (units #49 74) (MS#53, 58B) 20 feet 1376 September 30 Spawning Mainstem (units #1 74); SCB ND feet 1432 October 11 Spawning Mainstem (units #1 74); SCA, SCB, SCC ND feet 2444 November 9 Spawning Mainstem (units #1 74); SCA, SCB, SCC 12 (MS#58D) 5 10 feet 3597 November 13 Snorkel Mainstem (subsample) 6.7 (MS#3) 5 15 feet 2581 December 1 Spawning SCD side channel network* ND ND 3304 December 20 Snorkel Mainstem below unit #74 and SCD side channels** ND ND December 27 Snorkel SCC side channels (subsample night) (SCC1, SCC) 5 10 feet 2231 December 28 Snorkel SCC side channels (subsample day) (SCC1, SCC) feet Site of temperature measurements indicated in parentheses. MS#, mainstem habitat unit number; other listed sites are side channels (cf. Figs 2, 5, 7). 2 The maximum distance at which adult fish could be identified. For all snorkel surveys, an effective visibility of 10 feet was used to calculate fish densities (see Methods). 3 Average discharge in Skykomish River mainstem on date of survey; data from USGS gage *An attempt was also made on this date to survey spawning activity in mainstem habitat units adjacent to side channel network SCD (i.e. below the mouth of the Sultan River; Skykomish rm ), but poor visibility precluded the collection of redd and carcass data. **Snorkel survey could not be performed due to poor visibility. ND, no data collected. 46
2 1 Table 2. Proportional allocation subsampling protocol for seasonal mainstem snorkel survey (after EPA, 2002). River Segment I River Segment II Gold Bar (habitat unit #1) to Startup Startup (habitat unit #49) to Sultan (habitat unit #48) (habitat unit #74) Pool Riffle Glide Total (S) Pool Riffle Glide Total (S) Total count (H): % Total 1 : Number of units to subsample 2 (n): 13 7 Sampling fraction 3 (F): Subsample count 4 (I): % subsample total 5 : Randomly selected units for #23 #58A #70+71 subsample survey: #31 #68 #56 H 2 S 100. S N (closest integer). 3 R #41 #9 #43 #1 #26 #18 #21 #34 #48 #44 #10 n 4 S. H F (closest integer). H, number of habitat units within a given unit type; S, number of habitat units within river segment; R, number of habitat units within entire study reach (rm ); N, number of habitat units to be subsampled within entire study reach (selected as 20 for fall 2004 subsample survey). Note that the total number of mainstem units surveyed during summer 2004 (76) exceeds the number assigned to the most downstream unit in the study reach (#74). This discrepancy reflects the division of certain adjacent but distinct units using alphanumeric codes (e.g. #24A and #24B; cf. Fig. 3). #59 #73 #69 5 I n
3 Network Channel Table 3. Side channel snorkel-survey sites and habitat unit count Summer 2004 (day) Winter 2004 (day) Winter 2004 (night) Pool Riffle Glide Total Pool Riffle Glide Total Pool Riffle Glide Total SCB SCB SCB ND ND SCC SCC ND, no data collected. SCC SCC SBA SBA ND SBA ND SBA SBA ND ND Total:
4 Table 4. Summer 2004 Skykomish River braided reach mainstem and side channel fish densities Relative Density 1 (count m -2 ) Species Mainstem (76 habitat units) Side channel (52 habitat units) Mean S.E.M. Mean S.E.M. Adult Bull trout < < Chum salmon Coho salmon Cutthroat trout < < Rainbow trout Steelhead trout < < < < Stickleback Mountain whitefish Juvenile Bull trout < < Coho salmon Trout Mountain whitefish < < Other Summary 4 All fish species All salmonids, total All salmonids, adults All salmonids, juveniles ESA-listed (Chinook and bull trout) Densities reported as average daytime counts per square meter of survey area for all habitat units surveyed in summer 2004, including units in which no fish were observed. Side channel densities are pooled averages for side channel networks SCB and SCC. Zero densities (reflecting no fish observed in any habitat unit surveyed) have been omitted from the table. S.E.M., standard error of the mean. 2 Juvenile rainbow trout and/or cutthroat trout. 3 Unidentified non-salmonid juvenile. 4 These species categories summarize relative densities of juveniles and adults collectively, except where noted. The three salmonid categories do not include mountain whitefish (Prosopium williamsoni). 49
5 Table 5. Summer 2004 daytime fish counts for mainstem habitat units Species Pool (N=17) Riffle (N=33) Glide (N=26) All Units (N=76) Total Mean C.I. 1 Total Mean C.I. Total Mean C.I. Total Mean C.I. Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Coho salmon Trout Mountain whitefish Other All Fish % confidence interval around the mean. 2 Juvenile rainbow trout and/or cutthroat trout. 3 Unidentified non-salmonid juvenile. Note that zero counts have been omitted from Tables
6 Species Adult Bull trout Table 6. Fall 2004 daytime fish counts for mainstem habitat units (subsample) Pool (N=4) Riffle (N=9) Glide (N=7) All Units (N=20) Total Mean C.I. 1 Total Mean C.I. Total Mean C.I. Total Mean C.I. Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Coho salmon Trout Mountain whitefish Other 3 All Fish % confidence interval around the mean. 2 Juvenile rainbow trout and/or cutthroat trout. 3 Unidentified non-salmonid juvenile. 51
7 Table 7. Summer 2004 daytime fish counts for side channel network SCB habitat units Species Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Channel SCB Pool (N=3) Riffle (N=2) Glide (N=2) Total Mean C.I. 1 Total Mean C.I. Total Mean C.I Coho salmon Trout Mountain whitefish Other 3 All Fish % confidence interval around the mean. 2 Juvenile rainbow trout and/or cutthroat trout. 3 Unidentified non-salmonid juvenile. 52
8 Table 7. Summer 2004 fish counts for side channel network SCB habitat units (continued) Species Channel SCB1 Pool (N=8) Riffle (N=7) All Network SCB Units (N=22) Total Mean C.I. Total Mean C.I. Total Mean C.I. Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Coho salmon Trout Mountain whitefish Other All Fish
9 Table 8. Summer 2004 daytime fish counts for side channel network SCC habitat units receiving surface flow* Species Channel SCC SCC1 SCC3 Pool (N=7) Riffle (N=3) Pool (N=3) Pool (N=7) All SCC Surface Flow Units (N=20) Total Mean C.I. 1 Total Mean C.I. Total Mean C.I. Total Mean C.I. Total Mean C.I. Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Coho salmon Trout Mountain whitefish Other 3 All Fish *Fed from mainstem flow as opposed to groundwater discharge (cf. Table 9). No data are reported for channel SCC2 within the surface-flow system (Fig. 7) because the channel was dry during the survey. 1 95% confidence interval around the mean. 2 Juvenile rainbow trout and/or cutthroat trout. 3 Unidentified non-salmonid juvenile. 54
10 Table 9. Summer 2004 daytime fish counts for side channel network SCC habitat units in spring brook system Species Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Channel SBA SBA1 Pool (N=3) Riffle (N=1) Pool (N=1) Riffle (N=1) Total Mean C.I. 1 Total Mean C.I. Total Mean C.I. Total Mean C.I. Coho salmon Trout Mountain whitefish 17 Other 3 All Fish % confidence interval around the mean. 2 Juvenile rainbow trout and/or cutthroat trout. 3 Unidentified non-salmonid juvenile. 55
11 Table 9. Summer 2004 fish counts for side channel network SCC habitat units in spring brook system (continued) Species Channel All SCC Spring Brook SBA2 SBA3 SBA4 Units Pool (N=1) Pool (N=1) Pool (N=2) (N=10) Total Mean C.I. Total Mean C.I. Total Mean C.I. Total Mean C.I. Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Coho salmon Trout 351 Mountain whitefish Other All Fish
12 Table 10. Winter 2004 day and night fish counts for side channel network SCC habitat units Species Day (N=3) Channel SCC SCC1 SCC3 SBA SBA SBA3 Pool Pool Pool Pool Riffle Pool All Units Night (N=1) Day (N=1) Night (N=1) Day (N=7) Adult Bull trout Chum salmon Coho salmon Cutthroat trout Rainbow trout Steelhead trout Stickleback Mountain whitefish Juvenile Bull trout Coho salmon Trout Mountain whitefish Other 2 All Fish Night (N=3) Day (N=2) Night (N=2) Day (N=1) Night (N=1) Day (N=1) Night (N=1) Day (N=15) Night (N=9) Data tabulated as habitat-unit mean counts when N>1. 1 Juvenile rainbow trout and/or cutthroat trout. 2 Unidentified non-salmonid juvenile. 57
13 Habitat Unit # Unit Type Table 11. Summer 2004 fish counts for edge habitat within mainstem Edge Habitat Type Edge Habitat Location Unit Total Count Edge Habitat Proportion Within Edge Habitat (% Unit Total) 9 Riffle riprap Right bank Pool LWD + riprap Right bank Pool LWD Right bank Riffle LWD Left bank A Glide LWD Left bank Glide riprap Right bank Species with highest relative abundance (rank order) within edge habitat. LWD, large woody debris. Dominant Species 1 adult whitefish, juvenile trout juvenile coho, juvenile Chinook juvenile coho, juvenile Chinook juvenile unidentified salmonid, adult sucker juvenile coho, adult whitefish juvenile unidentified salmonid, juvenile trout 58
14 Table salmon redd and carcass counts in Skykomish River braided reach (present study) Chinook Chum Coho Unidentified sp. Survey Date Redd Count* Carcass Count Redd Count* Carcass Count Redd Count* Carcass Count Redd Count* Carcass Count 9/30/ /11/ /9/ /1/ Total *Sum of confirmed and presumed redds (see Methods). Table redd counts in Skykomish River (WDFW) 1 Survey Reach Count Redds/rm Mouth of Skykomish River Monroe, WA Monroe Confluence with Sultan River Sultan River Gold Bar, WA ( Big Eddy ) Big Eddy Sunset Falls Total Data from aerial surveys by the Washington Department of Fish and Wildlife between September and November Coverage included both the mainstem channel and side channel networks. The number of redds per river mile in each survey reach was calculated using approximate mainstem reach distance. The Sultan-to-Gold Bar reach is the same as the braided reach sampled in this study. Source: Jackson (2005a). 59
15 Species Table 14. Skykomish River braided reach salmon carcass measurements Fork Length (mean+s.d., inches) Adipose fin present (%)* Female:Male Ratio* Chinook 35.5± (86%) 0.70 (81%) Chum 31.4± (39%) 0.58 (38%) Coho 31.5± (100%) 0.50 (100%) 31.8±5.9 ND ND *Adipose fin presence and sex were determined for a subsample of Chinook and chum carcasses. Percentages of total carcass counts (cf. Table 12) upon which tabulated data are based appear in parentheses. ND, no data collected. 60
16 Table 15. Selected salmonid density data from summer snorkel surveys of northwest rivers River System Mean Relative Density 1 (count m -2 ) Coho salmon Rainbow trout Large mainstems (>50 m bankfull width) (Hillman and Chapman, 1989; Keefe et al., 1995; Jonasson et al., 1997) (Hillman and Chapman, 1989) Small mainstems (<50 m bankfull width) (Keefe et al., 1995; Jonasson et al., 1997; Scarnecchia and Roper, 2000) (Hankin and Reeves, 1988; Scarnecchia and Roper, 2000) (Hankin and Reeves, 1988; Scarnecchia and Roper, 2000) Side channels (G. Pess, unpublished*) (G. Pess, unpublished*) (G. Pess, unpublished*) 1 Mainstem densities reported as average counts per square meter of survey area for all habitat units surveyed, including units in which no fish were observed. Side channel values are adjusted relative densities (see text). All data are from summer snorkel surveys (July September) for age 0+ and 1+ juveniles; densities are pooled averages for different habitat unit types (cf. Bartz et al., 2006). *NOAA Fisheries, Northwest Fisheries Science Center; data from snorkel surveys on the Elwha River (WA). 61
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