Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Table 4.4. Summary <strong>of</strong> the available surface-water chemistry data for the Upper Fraser River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeo-MeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thAdult Upstream MigrationConventionalsHardness (mg/L) 208 208 0% 62.7 6.87 62.4 47.4 105 54.4 56.4 58.6 61.0 65.5 70.9 76.4Dissolved Oxygen (mg/L) 106 106 0% 10.0 1.03 9.97 7.90 13.3 8.40 8.80 9.43 9.90 10.3 11.0 12.0pH (pH units) 254 254 0% 7.91 0.298 7.91 5.90 8.59 7.27 7.60 7.90 8.00 8.08 8.10 8.15Residue Non-filterable (TSS; 106 105 1% 79.4 85.6 55.7 2.00 661 15.8 21.5 37.0 57.0 86.0 153 221mg/L)Temperature (C) 210 210 0% 13.7 4.77 12.3 0.500 24.7 7.00 9.00 11.0 13.0 16.0 21.0 22.3Turbidity (NTU) 219 218 0% 35.2 38.4 23.8 0.0500 355 5.18 8.24 16.0 26.0 40.0 62.8 86.7Nutrients (µg/L)Nitrate (NO 3 ), dissolved 70 70 0% 43.2 22.3 38.9 12 120 21 23 30 36.5 50.8 69 88.7Nitrogen - Nitrite, dissolved(NO 2 ) 78 42 46% 3.62 1.63 3.25 1 9 1 2 2.5 2.5 5 5 6Nitrogen Ammonia, dissolved 35 12 66% 4.5 3.29 3.7 2.5 13 2.5 2.5 2.5 2.5 5.5 9.6 11.6Phosphorus, total (stream) 133 128 4% 88.6 122 52.9 1 1140 9.8 22 35 56 98 163 214Major Ions (mg/L)Chloride, dissolved 241 215 11% 3.60 38.3 0.888 0.0500 595 0.250 0.250 0.600 0.880 1.30 2.20 3.00Fluoride, total 40 38 5% 0.0315 0.0146 0.0278 0.00500 0.0700 0.00975 0.0200 0.0200 0.0300 0.0325 0.0510 0.0600Sulfate, dissolved 128 128 0% 7.74 1.89 7.50 2.00 14.5 5.10 5.54 6.50 7.65 8.80 10.0 11.0Metals (µg/L)Aluminum, total 174 174 0% 1810 1530 1340 12 11400 359 540 900 1450 2200 3290 4560Arsenic, total 129 129 0% 0.784 0.7 NA 0.2 6.7 0.3 0.34 0.45 0.6 0.9 1.2 1.6Boron, total 47 45 4% 1.9 0.861 1.54 0.05 4.4 0.33 0.86 1.4 2 2.5 2.74 2.87Cadmium, total 151 151 0% 0.263 0.321 NA 0.013 2.7 0.018 0.02 0.045 0.2 0.3 0.5 0.85Chromium, total 166 166 0% 3.83 3.21 NA 0.2 19.1 0.812 1.1 1.73 2.99 4.7 7.3 9.93Cobalt, total 148 146 1% 1.58 1.49 NA 0.05 10.4 0.325 0.5 0.79 1.18 1.8 2.93 4.27Copper, total 168 168 0% 5.99 9.98 NA 1 118 1.5 1.8 2.58 3.7 6 10.5 16Iron, total 209 209 0% 3290 4360 2220 9.8 44000 670 945 1440 2300 3420 5740 8250Lead, total 168 160 5% 1.82 1.87 NA 0.1 16.2 0.235 0.358 0.8 1.3 2.13 3.5 5.21Manganese, total 167 167 0% 73.2 70.5 56.4 12.4 530 21.2 25.2 36.2 52.7 81.5 132 175T-98
Table 4.4. Summary <strong>of</strong> the available surface-water chemistry data for the Upper Fraser River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeo-MeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thMetals (µg/L; continued)Mercury, total 40 40 0% 19.1 17.2 8.15 0.05 91 0.0595 0.087 10 20 20 31 50.5Molybdenum, total 177 152 14% 1.6 3.2 NA 0.05 20 0.259 0.3 0.4 0.5 0.617 5 5Nickel, total 148 144 3% 5.13 4.75 NA 0.3 26.6 1.34 1.8 2.51 3.71 5.6 9.69 15.1Selenium, total 124 88 29% 0.11 0.0973 NA 0.025 0.6 0.025 0.025 0.05 0.095 0.1 0.2 0.3Silver, total 102 69 32% 0.0537 0.0837 NA 0.0005 0.8 0.005 0.006 0.012 0.05 0.061 0.1 0.1Chlorophenols (µg/L)Dichlorophenols 27 0 100% 0.025 7.980E-10 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025Monochlorophenols 27 0 100% 0.025 7.98E-10 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025Pentachlorophenol 27 0 100% 0.025 7.98E-10 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025Tetrachlorophenols 27 0 100% 0.025 7.98E-10 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025Trichlorophenols 27 0 100% 0.025 7.98E-10 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025 0.025Other (µg/L)Cyanide WAD 1 0 100% 0.25 NA 0.25 0.25 0.25 0.25 0.25 0.25 0.25 0.25 0.25 0.25Phenols 29 14 52% 2.48 2.25 1.84 1 10 1 1 1 1 3 5.2 6.6Smolt OutmigrationConventionalsHardness (mg/L) 116 116 0% 60.6 4.50 60.5 51.5 87.9 55.1 56.1 58.2 60.3 62.4 64.2 65.3Dissolved Oxygen (mg/L) 61 61 0% 10.5 1.03 10.4 8.40 13.3 9.20 9.30 9.70 10.2 11.0 12.0 12.0pH (pH units) 138 138 0% 7.87 0.322 7.86 6.60 8.30 7.09 7.37 7.89 8.00 8.01 8.10 8.10Residue Non-filterable55 55 0% 151 125 119 35.0 661 58.5 63.8 73.5 101 171 314 391(TSS; mg/L)Temperature (C) 118 118 0% 11.2 6.17 8.80 0.500 24.7 0.925 4.00 8.00 11.0 13.0 22.5 22.9Turbidity (NTU) 119 119 0% 55.5 44.6 42.1 0.0600 249 19.8 21.8 28.0 40.0 66.7 93.3 161Nutrients (µg/L)Nitrate (NO 3 ), dissolved 39 39 0% 98.8 48.9 88.5 32 254 46.5 52.6 58.5 90 122 151 172Nitrogen - Nitrite, dissolved(NO 2 ) 43 24 44% 3.64 1.37 3.35 1 6 2.05 2.5 2.5 4 5 5 5Nitrogen Ammonia, dissolved 18 10 44% 6.28 4.18 5.05 2.5 16 2.5 2.5 2.5 6 8.75 11.6 13.5T-99
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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 4.21. Evaluation of</
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Table 4.32. Frequency of</s
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Table 4.45. Summary of</str
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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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