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 95thAdult Upstream MigrationConventionalsHardness (mg/L) 20 20 0% 30.7 6.63 30.2 26.8 55.5 26.8 27.0 27.6 28.1 29.9 37.2 38.5Dissolved Oxygen (mg/L) 2 2 0% 10.7 0.707 10.7 10.2 11.2 10.3 10.3 10.5 10.7 11.0 11.1 11.2pH (pH units) 21 21 0% 7.50 0.506 7.48 6.00 7.90 6.20 7.00 7.50 7.70 7.80 7.80 7.80Residue Non-filterable (TSS; mg/L) 14 14 0% 10.5 18.5 5.17 1.00 73.0 1.65 2.00 2.25 4.00 9.00 14.1 35.3Temperature (C) 7 7 0% 13.0 1.38 12.9 10.5 15.0 11.1 11.7 12.8 13.0 13.5 14.4 14.7Turbidity (NTU) 19 19 0% 13.7 13.0 9.80 1.10 47.4 5.15 5.86 6.38 9.30 11.8 36.4 42.5Nutrients (µg/L)Nitrogen - Nitrite, dissolved (NO 2 ) 2 0 100% 1.75 1.06 1.58 1 2.5 1.08 1.15 1.38 1.75 2.13 2.35 2.43Phosphorus, total (stream) 25 22 12% 27.2 34.9 14.2 1 152 1 2.2 12 16 22 65.8 95.4Major Ions (mg/L)Chloride, dissolved 2 1 50% 0.425 0.247 0.387 0.250 0.600 0.268 0.285 0.338 0.425 0.513 0.565 0.583Sulfate, dissolved 22 21 5% 6.38 3.26 5.47 0.250 19.5 4.53 5.01 5.38 6.05 6.60 6.99 7.48Metals (µg/L)Aluminum, total 12 12 0% 415 350 259 2.6 1460 152 276 296 345 382 507 942Arsenic, total 15 14 7% 0.41 0.191 0.357 0.05 0.8 0.225 0.3 0.3 0.4 0.45 0.68 0.8Boron, total 2 2 0% 13.5 0.707 13.5 13 14 13.1 13.1 13.3 13.5 13.8 13.9 14Cadmium, total 15 5 67% 0.00933 0.00942 0.00724 0.005 0.04 0.005 0.005 0.005 0.005 0.01 0.016 0.026Chromium, total 15 4 73% 0.22 0.224 0.155 0.1 0.7 0.1 0.1 0.1 0.1 0.2 0.62 0.7Cobalt, total 15 13 13% 0.297 0.405 0.113 0.0025 1.28 0.0025 0.0155 0.087 0.184 0.204 0.902 1.26Copper, total 17 17 0% 2.8 3.1 1.93 0.87 11 0.87 0.87 1.28 1.48 2 6.78 10.2Iron, total 2 2 0% 561 290 522 356 766 377 397 459 561 664 725 746Lead, total 17 15 12% 0.879 1.93 0.197 0.005 6 0.049 0.066 0.09 0.13 0.5 2.73 6Manganese, total 16 15 6% 17.3 18.9 12.6 5 66.2 6.63 7.29 8.81 10.5 13.8 41.1 64.3Molybdenum, total 15 14 7% 0.93 0.286 0.771 0.025 1.36 0.47 0.752 0.965 0.98 1.03 1.05 1.14Nickel, total 14 12 14% 0.628 0.887 0.296 0.025 2.7 0.025 0.0685 0.223 0.295 0.448 2.08 2.68Selenium, total 15 1 93% 0.107 0.0258 0.105 0.1 0.2 0.1 0.1 0.1 0.1 0.1 0.1 0.13Silver, total 15 0 100% 0.01 2.11E-10 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.01T-122
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 95thJuvenile RearingConventionalsHardness (mg/L) 7 7 0% 23.9 2.84 23.8 21.0 28.3 21.1 21.2 21.7 23.2 25.9 27.5 27.9Dissolved Oxygen (mg/L) 6 6 0% 10.3 1.59 10.2 8.80 12.8 8.85 8.90 9.10 9.90 11.3 12.2 12.5pH (pH units) 18 18 0% 7.36 0.273 7.35 6.90 7.70 6.99 7.00 7.13 7.35 7.60 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) 4 4 0% 8.00 4.45 6.28 1.50 11.5 2.63 3.75 7.13 9.50 10.4 11.1 11.3Turbidity (NTU) 6 6 0% 13.6 4.94 12.8 6.50 21.0 7.88 9.25 12.0 12.5 16.0 19.0 20.0Nutrients (µg/L)Nitrate (NO 3 ), dissolved 4 2 50% 45 63.5 23 10 140 10 10 10 15 50 104 122Nitrogen - Nitrite, dissolved (NO 2 ) 12 2 83% 2.42 0.469 2.35 1 3 1.83 2.5 2.5 2.5 2.5 2.5 2.73Phosphorus, total (stream) 11 11 0% 12.2 5.95 11.1 6 24 6.5 7 9 10 12 23 23.5Major Ions (mg/L)Sulfate, dissolved 17 17 0% 7.21 1.22 7.11 5.50 9.50 5.90 6.00 6.20 7.00 7.80 9.24 9.34Metals (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 0.05Spawning & IncubationConventionalsHardness (mg/L) 5 5 0% 24.5 3.27 24.3 21.0 28.3 21.1 21.1 21.3 24.8 26.9 27.7 28.0Dissolved Oxygen (mg/L) 5 5 0% 10.6 1.57 10.5 9.00 12.8 9.08 9.16 9.40 10.4 11.6 12.3 12.6T-123
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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 4.35. 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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