Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Table 4.11. Summary <strong>of</strong> the available surface-water chemistry data for the Chilko River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeometricMeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thConventionals (continued)pH (pH units) 16 16 0% 7.34 0.283 7.34 6.90 7.70 6.98 7.00 7.10 7.35 7.63 7.70 7.70Residue Non-filterable (TSS; mg/L) 11 10 9% 9.36 8.49 6.58 2.00 26.0 2.00 2.00 4.00 6.00 12.0 24.0 25.0Temperature (C) 3 3 0% 7.67 5.39 5.57 1.50 11.5 2.35 3.20 5.75 10.0 10.8 11.2 11.4Turbidity (NTU) 4 4 0% 15.5 4.36 15.1 12.0 21.0 12.0 12.0 12.0 14.5 18.0 19.8 20.4Nutrients (µg/L)Nitrate (NO 3 ), dissolved 3 2 33% 56.7 72.3 30.4 10 140 11 12 15 20 80 116 128Nitrogen - Nitrite, dissolved (NO 2 ) 11 2 82% 2.41 0.491 2.34 1 3 1.75 2.5 2.5 2.5 2.5 2.5 2.75Phosphorus, total (stream) 10 10 0% 12.7 6 11.6 6 24 6.9 7.8 10 11 12 23.1 23.6Major Ions (mg/L)Sulfate, dissolved 15 15 0% 7.28 1.27 7.18 5.50 9.50 5.85 6.00 6.35 7.00 8.00 9.26 9.36Metals (µg/L)Aluminum, total 10 10 0% 1550 1030 1320 660 3490 692 723 1080 1170 1440 3410 3450Arsenic, total 8 4 50% 0.75 0.267 0.707 0.5 1 0.5 0.5 0.5 0.75 1 1 1Boron, total 10 3 70% 27 25.6 16.8 4 76 4 4 8 20 30.5 68.8 72.4Chromium, total 4 4 0% 3 1.41 2.78 2 5 2 2 2 2.5 3.5 4.4 4.7Cobalt, total 10 1 90% 1.95 0.762 1.86 1.5 4 1.5 1.5 1.5 1.75 2 2.2 3.1Copper, total 1 1 0% 1 NA 1 1 1 1 1 1 1 1 1 1Iron, total 11 11 0% 1220 710 1080 562 2610 599 635 863 960 1170 2590 2600Lead, total 1 0 100% 0.5 NA 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5Molybdenum, total 11 1 91% 1.99 0.0302 1.99 1.9 2 1.95 2 2 2 2 2 2Silver, total 4 0 100% 0.05 NA 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.05Smolt OutmigrationConventionalsHardness (mg/L) 12 12 0% 34.4 10.7 33.1 26.8 57.3 27.2 27.5 27.8 29.7 33.9 53.7 56.3Dissolved Oxygen (mg/L) 1 1 0% 11.2 NA 11.2 11.2 11.2 11.2 11.2 11.2 11.2 11.2 11.2 11.2pH (pH units) 10 10 0% 7.57 0.564 7.55 6.00 7.90 6.68 7.35 7.63 7.80 7.80 7.81 7.86Residue Non-filterable (TSS; mg/L) 8 8 0% 15.6 23.5 8.60 2.00 73.0 2.70 3.40 5.50 8.00 10.5 32.4 52.7Temperature (C) 3 3 0% 13.7 1.15 13.6 13.0 15.0 13.0 13.0 13.0 13.0 14.0 14.6 14.8Turbidity (NTU) 11 11 0% 17.7 15.7 12.8 3.86 47.4 5.17 6.48 7.45 11.1 23.7 42.0 44.7T-124
Table 4.11. Summary <strong>of</strong> the available surface-water chemistry data for the Chilko River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeometricMeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thNutrients (µg/L)Phosphorus, total (stream) 11 9 18% 0.0405 0.0469 0.0170 0.00100 0.152 0.00100 0.00100 0.0105 0.0230 0.0505 0.0990 0.126Major Ions (mg/L)Sulfate, dissolved 11 11 0% 5.99 0.936 5.92 4.30 7.50 4.65 5.00 5.45 5.90 6.60 7.00 7.25Metals (µg/L)Aluminum, total 8 8 0% 485 407 397 172 1460 210 248 297 371 432 801 1130Arsenic, total 9 9 0% 0.522 0.172 0.499 0.3 0.8 0.34 0.38 0.4 0.5 0.5 0.8 0.8Boron, total 1 1 0% 14 NA 14 14 14 14 14 14 14 14 14 14Cadmium, total 9 5 44% 0.0122 0.0115 0.00926 0.005 0.04 0.005 0.005 0.005 0.01 0.01 0.024 0.032Chromium, total 9 4 56% 0.3 0.265 0.208 0.1 0.7 0.1 0.1 0.1 0.1 0.5 0.7 0.7Cobalt, total 9 9 0% 0.44 0.473 0.294 0.135 1.28 0.139 0.144 0.165 0.201 0.381 1.26 1.27Copper, total 11 11 0% 3.54 3.68 2.32 0.87 11 0.93 0.99 1.18 1.48 4.46 10 10.5Iron, total 1 1 0% 766 NA 766 766 766 766 766 766 766 766 766 766Lead, total 11 11 0% 1.26 2.35 0.305 0.06 6 0.08 0.1 0.105 0.13 0.525 6 6Manganese, total 10 9 10% 22.8 22.7 15.9 5 66.2 6.13 7.27 8.62 14.4 19.5 63.9 65Molybdenum, total 9 9 0% 1.04 0.187 1.02 0.66 1.36 0.78 0.9 1.02 1.03 1.05 1.23 1.3Nickel, total 9 9 0% 0.922 1.01 0.606 0.25 2.7 0.27 0.29 0.34 0.48 0.69 2.68 2.69Selenium, total 9 1 89% 0.111 0.0333 0.108 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.12 0.16Silver, total 9 0 100% 0.01 1.61E-10 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01n = number <strong>of</strong> samples; detect = detected; SD = standard deviation; NA = no data available; TSS = total suspended solids.No data were available for the following areas <strong>of</strong> interest within the Fraser River Basin: Harrison River, Nahatlatch, Seton-Portage.One-half the detection limit was substituted for non-detect values in the distribution calculations.The minimum value shown is the lower <strong>of</strong> one-half the detection limit or the lowest detectable measurement.The maximum value shown is the higher <strong>of</strong> one-half the detection limit or the highest detectable measurement.T-125
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February 2011technical report 2<str
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thresholds), which represent lowest
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Table of ContentsE
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5.5 Summary of the
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List of TablesTabl
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Table 4.17Table 4.18Table 4.19Table
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Table 4.47Table 4.48Table 4.49Table
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Table 6.4Table 8.1Compounds for Nat
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Figure 3.17 Map of
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Figure 5.20 Late Stuart Sockeye Sal
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List of Acronyms2,
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AcknowledgementsThe authors would l
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To assist it in fulfilling this man
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• Development of
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Chapter 2 Geographic and Temporal S
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life history of th
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• Pitt River Area of</str
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Chapter 3 Inventory of</str
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and Paper Mills - Canfor Pulp Limit
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3.1.1.2 Sawmills, Plywood Mills and
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(ENKON Environmental Ltd. 2001). Co
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Effluent toxicity was also included
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2011 for more information on the lo
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facilities identified in Table 3.11
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Inc.), poultry processing facilitie
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• Polycyclic aromatic hydrocarbon
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3.1.1.11 Municipal Wastewater Treat
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• Personal care products (fragran
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with oxytetracycline, ormetoprim, a
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In summary, the contaminants that c
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insecticides, such as phorate, terb
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3.1.2.4 Runoff fro
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the substances most amenable to lon
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• Plastic-related compounds (i.e.
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were used in the effects and exposu
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warrants further assessment to dete
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• Data collected for migration co
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Hazard quotients were calculated fo
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Many other substances have the pote
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Chapter 5 Evaluation of</st
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For surface water and sediment, the
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3. For hardness-dependent water qua
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• 2,3,7,8-TCDD toxic equivalents
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concern by area of
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0.05 mg/L; Glew and Hames 1971). As
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least time rearing in freshwater ha
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The results of thi
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Interest and in the South Thompson
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• Polychlorinated dibenzo-p-dioxi
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glycoproteins, polypeptides, peptid
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In-use herbicides in the Fraser Riv
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and home wood heating; Johannessen
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Pulp and paper mills, saw mills, an
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salinity tolerance were significant
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and gonadosomatic index scores were
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the lowest observed effect concentr
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Spitsbergen et al. (1991) reported
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Chakravorty et al. (1992) observed
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observed in saltwater gobies (Chasm
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(See Chapters 4 and 5 for further i
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emoval efficiency of</stron
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point and non-point source discharg
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Location of NatalS
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Nevertheless, it is possible that e
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concern relative to human or enviro
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these substances to aquatic ecosyst
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• Alkylphenol ethoxylates (APEOs;
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chemicals of poten
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productivity data, it is apparent t
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• Sufficiency - For a cause and e
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infection by various disease agents
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magnitude, and spatial extent <stro
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potential concern were documented a
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pathways and the intensity and exte
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Chilko River, Quesnel River, Nechak
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• The majority of</strong
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7.4.6 Information on Interactive <s
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• Development of
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8.4 Preliminary Evaluation
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8.5 Evaluation of
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the low returns of
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8.9 RecommendationsThis evaluation
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Chapter 9 References CitedAdams, R.
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Braune, B., D. Muir, B. DeMarch, M.
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EIP Associates. 1997. Polychlorinat
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Gallaugher, P. and L. Wood (Eds). P
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Hinch, S.G. and E.G. Martins. 2011.
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Kemble, N.E., D.K. Hardesty, C.G. I
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MacLatchy, D., L. Peters, J. Nickle
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Milston, R.H., M.S. Fitzpatrick, A.
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Peterman, R.M., D. Marmorek, B. Bec
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Smith, D.B., R.A. Zielinski, H.E. T
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USACE (U.S. Army Corps of</
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Walker, M.K., J.M. Spitsbergen, J.R
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Table 2.1. Overview of</str
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Table 2.2. Sampling sites for Early
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Table 2.3. Sampling sites for summe
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Table 2.4. Sampling sites for river
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Table 3.1. Listing of</stro
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Table 3.2. Chemicals of</st
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Table 3.8. Major pipelines transpor
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Table 3.10. Locations of</s
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Table 3.11. Listing of</str
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Table 3.16. List of</strong
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Table 3.17. List of</strong
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Table 3.18. Location of</st
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Table 3.20. Summary of</str
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Table 4.36. Frequency of</s
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Table 4.51. Evaluation of</
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Table 4.53. Identification
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Table 5.1. Selected toxicity refere
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Table 5.2. Selected toxicity refere
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Table 5.3. Exposure point concentra
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Table 5.9. Hazard quotients <strong
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Table 5.11. Hazard quotients <stron
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Table 5.19. Hazard quotients <stron
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Table 5.23. Mean concentrations <st
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Table 6.2. Effects
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Table 6.3. Field studies of
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Table 6.4. Compounds for National r
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Table 8.1. Inventory of</st
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Figures
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Figure 5.1. Water Quality Index sco
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Figure 5.3. Fraser River Sockeye Sa
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Figure 5.5. Pitt Sockeye Salmon Pro
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Figure 5.7. Weaver Sockeye Salmon P
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Figure 5.9. Cultus Sockeye Salmon P
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Figure 5.11. Portage Sockeye Salmon
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Figure 5.13. Fennell Sockeye Salmon
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Figure 5.15. Late Shuswap Sockeye S
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Figure 5.17. Chilko Sockeye Salmon
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Figure 5.19. Early Stuart Sockeye S
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Figure 5.21. Stellako Sockeye Salmo
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Figure 5.23. Bowron Sockeye Salmon
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Appendices
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SW4 Deliverables4.1 The Contractor
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obtained on one species, sometimes
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• For substances for which the se
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WeaknessesThere is a lot of
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Pg 110 Ln 4189 - now called Listene
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the potential effects of</s
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A-14
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4. Fish processing plants are fewer
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Appendix 3. Environmental Data Sour
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4. Keyword searches for water quali
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A3.5 Contaminant Spill ReportsData
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River Pulp, Kamloops Cellulose Fibr
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Table A3.1. Water quality stations
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Table A3.1. Water quality stations
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Appendix 4. Data Treatment and Meth
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when multiple samples were reported
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$ Early rearing of
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i) The number of t
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In addition, some sockeye salmon (e
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• Selecting probable effect conce
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deBruyn, A.M., H. deBruyn, M.G. Iko
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Appendix 5. Data description and so
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Potential Effects of Contaminants on Fraser River Sockeye Salmon

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