Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Table 4.48. Summary <strong>of</strong> hazards posed to sockeye salmon exposed to surface water during the adult upstream migration life stage within the Fraser RiverBasin (maximum hazard quotients are reported for each chemical <strong>of</strong> potential concern).Area <strong>of</strong> InterestChemical <strong>of</strong> <strong>Potential</strong>ConcernLower Fraser RiverUpper Fraser RiverPitt RiverHarrison RiverCultus LakeKakawa LakeNahatlatchSeton-PortageLower Thompson RiverNorth Thompson RiverSouth Thompson RiverChilko RiverQuesnel RiverNechako RiverBowron RiverReferenceFraser River BasinConventionalspH 1 3.42 1.12 0 ND 0 0 ND ND 0 1.07 1.07 1.08 0 1.06 ND 0 3.42Residue Non-filterable(TSS) 12.1 26.4 6.16 ND 2.04 0.560 ND ND 10.4 2.56 2.92 2.92 18.2 1.20 ND 0.840 26.4Turbidity 195 178 19.0 ND 90.0 1.65 ND ND 42.0 11.0 3.30 23.7 26.0 15.0 ND 11.1 195NutrientsAmmonia, dissolved 0.610 0.0384 0.0352 ND 0.0515 0.00856 ND ND 0.533 0.0954 0.126 ND 0.0260 0.225 ND ND 0.610Nitrate (NO 3 ), dissolved 0.0369 0.0414 ND ND 1.45 0.0345 ND ND 0.0379 0.0276 0.0324 ND 0.0310 0.0345 ND 0.0293 1.45Nitrogen-Nitrite,0.667 0.150 0.100 ND 3.95 0.300 ND ND 0.150 0.100 0.0833 0.0417 0.0417 0.233 ND 0.367 3.95dissolved (NO 2 )Phosphorus, total (lake) ND ND ND ND ND ND ND ND 53.3 ND ND ND ND ND ND ND 53.3Phosphorus, total (stream) 90.6 228 ND ND 38.0 3.20 ND ND 87.4 14.4 12.6 30.4 2.00 42.2 ND 20.6 228Major IonsChloride, dissolved 0.0148 2.59 ND ND 0.0783 0.00435 ND ND 0.0326 0.0174 0.0287 0.00261 0.0113 0.0426 ND 0.0739 2.59Fluoride, total 0.350 0.233 ND ND ND ND ND ND 0.950 0.900 0.300 ND ND 0.800 ND 0.333 0.950Sulfate, dissolved 0.140 0.145 ND ND 0.300 0.106 ND ND 0.990 0.330 0.450 0.195 3.20 0.0700 ND 0.190 3.20MetalsAluminum, total 181 114 18.2 ND 2.50 ND ND ND 14.2 17.7 6.90 14.6 67.8 53.2 ND 5.22 181Arsenic, total 0.418 1.34 ND ND 0.256 0.500 ND ND 8.00 0.500 0.500 0.160 0.200 0.300 ND 0.440 8.00T-198
Table 4.48. Summary <strong>of</strong> hazards posed to sockeye salmon exposed to surface water during the adult upstream migration life stage within the Fraser RiverBasin (maximum hazard quotients are reported for each chemical <strong>of</strong> potential concern).Area <strong>of</strong> InterestChemical <strong>of</strong> <strong>Potential</strong>ConcernLower Fraser RiverUpper Fraser RiverPitt RiverHarrison RiverCultus LakeKakawa LakeNahatlatchSeton-PortageLower Thompson RiverNorth Thompson RiverSouth Thompson RiverChilko RiverQuesnel RiverNechako RiverBowron RiverReferenceFraser River BasinMetals (continued)Boron, total 0.0825 0.00367 ND ND 0.0717 ND ND ND 0.0167 0.0167 0.0583 0.0117 1.85 0.00350 ND 0.00117 1.85Cadmium, total 82.4 159 ND ND 0.647 ND ND ND 58.8 588 412 2.35 23.5 118 ND 235 588Chromium, total 44.0 19.1 ND ND 24.0 ND ND ND 27.0 20.0 40.0 0.700 8.00 20.7 ND 16.9 44.0Cobalt, total 2.29 2.60 ND ND 0.375 ND ND ND 2.00 3.25 3.50 0.320 0.375 0.200 ND 0.300 3.50Copper, total 79.5 59.0 ND ND 0.400 1.50 ND ND 10.0 10.5 9.00 5.50 12.0 365 ND 54.0 365Iron, total 54.7 147 8.43 ND 5.53 1.67 ND ND 6.93 7.63 2.73 2.55 37.7 4.90 ND 2.53 147Lead, total 8.00 8.10 ND ND 0.114 2.00 ND ND 2.00 60.0 60.0 6.00 0.500 18.8 ND 2.80 60.0Manganese, total 0.410 0.606 ND ND 0.0787 0.0289 ND ND 0.0136 0.0645 0.0431 0.0911 0.322 0.0950 ND 0.0360 0.606Mercury, total 2000 4550 ND ND ND ND ND ND ND ND ND ND 7250 26500 ND 2500 26500Molybdenum, total 0.411 0.274 0.0685 ND 0.0274 0.00822 ND ND 0.685 0.274 0.137 0.0186 0.425 0.959 ND 0.00685 0.959Nickel, total 1.32 0.880 ND ND 0.235 0.200 ND ND 0.200 0.400 4.00 0.108 0.280 3.60 ND 0.172 4.00Selenium, total 0.400 0.600 ND ND 0.240 ND ND ND 0.100 60.0 60.0 0.200 0.800 1.20 ND 0.970 60.0Silver, total 7.00 8.00 ND ND 0.0300 ND ND ND ND ND ND 0.100 0.500 403 ND 6.00 403ChlorophenolsDichlorophenols 0.0125 0.0125 ND ND ND ND ND ND ND ND ND ND ND ND ND ND 0.0125Monochlorophenols 0.00357 0.00357 ND ND ND ND ND ND ND ND ND ND ND ND ND ND 0.00357Pentachlorophenol 0.0500 0.0500 0.100 ND ND ND ND ND ND ND ND ND ND ND ND ND 0.100Tetrachlorophenols 0.0250 0.0250 0.0500 ND ND ND ND ND ND ND ND ND ND ND ND ND 0.0500Trichlorophenols 0.00139 0.00139 0.00278 ND ND ND ND ND ND ND ND ND ND ND ND ND 0.00278T-199
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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 3.23. Estimated annual contam
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Table 3.28. Inventory of</s
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Table 4.1. Selected toxicity screen
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Table 4.2. Selected toxicity screen
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Table 4.3. Summary of</stro
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Table 4.19. Evaluation of</
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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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