Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Table 4.7. Summary <strong>of</strong> the available surface-water chemistry data for the Kakawa Lake Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeometricMeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thConventionals (continued)Residue Non-filterable (TSS; mg/L) 4 4 0% 7.50 4.93 6.09 2.00 14.0 2.75 3.50 5.75 7.00 8.75 11.9 13.0Temperature (C) 6 6 0% 8.28 3.97 7.51 4.00 15.0 4.13 4.25 5.50 8.50 9.03 12.1 13.6Turbidity (NTU) 2 2 0% 14.4 19.2 4.73 0.800 28.0 2.16 3.52 7.60 14.4 21.2 25.3 26.6Nutrients (µg/L)Nitrate (NO 3 ), dissolved 4 4 0% 77.5 17.1 76.1 60 100 61.5 63 67.5 75 85 94 97Nitrogen - Nitrite, dissolved (NO 2 ) 6 0 100% 2.5 NA 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5Nitrogen Ammonia, dissolved 4 3 25% 4.88 1.65 4.61 2.5 6 2.88 3.25 4.38 5.5 6 6 6Phosphorus, total (stream) 4 4 0% 16 15.7 11.5 5 39 5.3 5.6 6.5 10 19.5 31.2 35.1Major Ions (mg/L)Chloride, dissolved 6 4 33% 0.450 0.173 0.420 0.250 0.700 0.250 0.250 0.313 0.500 0.500 0.600 0.650Sulfate, dissolved 5 1 80% 3.28 1.74 3.02 2.50 6.40 2.50 2.50 2.50 2.50 2.50 4.84 5.62Metals (µg/L)Copper, total 4 2 50% 1.5 1.22 1.11 0.5 3 0.5 0.5 0.5 1.25 2.25 2.7 2.85Iron, total 3 3 0% 300 200 247 100 500 120 140 200 300 400 460 480Lead, total 3 1 67% 1 0.866 0.794 0.5 2 0.5 0.5 0.5 0.5 1.25 1.7 1.85Manganese, total 4 2 50% 22.5 18.9 17.8 10 50 10 10 10 15 27.5 41 45.5Nickel, total 4 1 75% 6.25 2.5 5.95 5 10 5 5 5 5 6.25 8.5 9.25n = 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-110
Table 4.8. Summary <strong>of</strong> the available surface-water chemistry data for the Lower Thompson River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeometricMeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thAdult Upstream MigrationConventionalsHardness (mg/L) 95 95 0% 64.6 45.7 53.2 30 203 31.1 32.1 33.6 37.4 88.3 132 170Dissolved Oxygen (mg/L) 69 69 0% 9.79 1.59 9.67 4.7 16 8.08 8.46 9.2 9.7 10 11.5 12pH (pH units) 313 313 0% 8.18 0.373 8.17 7 8.95 7.5 7.6 7.9 8.24 8.4 8.6 8.7Residue Non-filterable (TSS; mg/L) 152 138 9% 24.8 42.3 10 0.5 260 2 2.5 4 7 24 66.3 128Temperature (C) 174 174 0% 15.8 3.42 15.4 5 28 11 11.5 14 15.6 18 20 21Turbidity (NTU) 220 220 0% 7.58 14.5 3 0.1 84 0.677 0.87 1.21 2.38 5.3 20.5 44.3Nutrients (µg/L)Nitrate (NO 3 ), dissolved 81 47 42% 23.4 27.8 8.17 1 110 1 1 1 10 40 60 80Nitrogen - Nitrite, dissolved (NO 2 ) 148 11 93% 2.68 1.12 NA 1 9 2.18 2.5 2.5 2.5 2.5 2.5 5Nitrogen Ammonia, dissolved 127 58 54% 12.8 20.8 6.14 2.5 117 2.5 2.5 2.5 2.5 12 30.4 52.1Phosphorus, total (lake) 53 53 0% 53.7 108 33.4 4 800 9.2 13.4 22 33 52 77.6 102Phosphorus, total (stream) 236 230 3% 39.8 58.2 NA 1.5 437 5 7 12 21 40.3 89 157Major Ions (mg/L)Chloride, dissolved 231 227 2% 2.48 1.83 1.78 0.15 7.5 0.3 0.4 1.2 1.9 3.3 5.5 6.25Fluoride, total 14 10 29% 0.0814 0.049 0.0705 0.025 0.19 0.0413 0.05 0.05 0.061 0.09 0.159 0.184Sulfate, dissolved 185 182 2% 13.4 11 10.8 2.5 99 5 5.3 6.5 9.5 17.4 23.4 31.8Metals (µg/L)Aluminum, total 16 14 13% 361 379 200 30 1420 30 40 77.5 275 495 750 955Arsenic, total 4 2 50% 11.3 19.2 2.66 0.2 40 0.545 0.89 1.93 2.5 11.9 28.8 34.4Boron, total 10 0 100% 17 6.32 15.2 5 20 5 5 20 20 20 20 20Cadmium, total 1 1 0% 1 NA 1 1 1 1 1 1 1 1 1 1Chromium, total 13 13 0% 8.17 7.8 4.79 0.2 27 1.28 2 2 5 10 18 22.8Cobalt, total 10 1 90% 2.3 2.1 1.74 0.5 8 0.5 0.5 2 2 2 2.6 5.3Copper, total 11 8 27% 3.05 5.84 1.28 0.5 20 0.5 0.5 0.75 1 1 6 13Iron, total 26 26 0% 434 465 241 14 2080 26.3 43 118 265 630 910 1180Lead, total 9 2 78% 0.722 0.507 0.63 0.5 2 0.5 0.5 0.5 0.5 0.5 1.2 1.6Manganese, total 16 5 69% 6.63 2.28 6.3 5 10 5 5 5 5 9.25 10 10Molybdenum, total 25 6 76% 5.88 9.72 2.8 0.1 50 0.25 0.35 2 5 5 10 10T-111
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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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Page 251 and 252: Table 3.18. Location of</st
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Table 4.28. 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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