Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Table 4.12. Summary <strong>of</strong> the available surface-water chemistry data for the Quesnel River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeometricMeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thMetals (µg/L)Aluminum, total 26 26 0% 214 413 72.9 13.9 2060 19.5 20.6 25.1 32.8 302 485 529Arsenic, total 28 28 0% 0.313 0.134 0.294 0.21 0.88 0.224 0.23 0.23 0.26 0.35 0.44 0.447Boron, total 28 28 0% 4.6 1.42 4.36 2.1 6.5 2.24 2.37 3.65 4.85 5.85 6.26 6.47Cadmium, total 28 28 0% 0.0155 0.0149 0.012 0.003 0.081 0.00535 0.006 0.008 0.01 0.0175 0.0283 0.031Chromium, total 28 28 0% 0.581 0.882 0.325 0.111 4.63 0.116 0.127 0.145 0.2 0.809 1.18 1.22Cobalt, total 28 28 0% 0.184 0.321 0.0883 0.021 1.68 0.0281 0.032 0.0408 0.0485 0.248 0.38 0.424Copper, total 10 10 0% 1.13 0.632 1 0.63 2.26 0.648 0.666 0.723 0.79 1.23 2.26 2.26Iron, total 28 28 0% 373 547 220 72.3 2890 79.5 90.7 108 151 551 720 744Lead, total 10 9 10% 0.0607 0.0813 0.0287 0.003 0.214 0.00633 0.0102 0.0178 0.022 0.044 0.212 0.213Manganese, total 10 10 0% 13 9.06 11 6.59 31.6 7.01 7.44 7.8 8.53 11.6 28.4 30Molybdenum, total 28 28 0% 0.829 0.115 0.821 0.531 1.08 0.647 0.701 0.751 0.842 0.913 0.938 0.966Nickel, total 10 10 0% 0.755 0.518 0.64 0.41 1.74 0.41 0.41 0.44 0.455 0.795 1.67 1.7Selenium, total 28 28 0% 0.299 0.051 0.295 0.2 0.46 0.244 0.25 0.268 0.29 0.313 0.349 0.383Silver, total 28 23 18% 0.0053 0.00729 0.00278 5E-04 0.037 0.0005 0.0005 0.001 0.003 0.0055 0.0109 0.013Smolt OutmigrationConventionalsHardness (mg/L) 17 17 0% 58.7 25.4 55.7 43.0 152 43.0 43.2 48.0 55.2 56.8 65.8 92.5pH (pH units) 17 17 0% 7.82 0.243 7.81 7.33 8.17 7.43 7.47 7.68 7.86 7.94 8.11 8.13Residue Non-filterable (TSS; mg/L) 18 18 0% 42.5 44.4 23.8 2.00 166 2.85 6.50 11.3 24.5 62.0 102 116Temperature (C) 17 17 0% 12.3 4.00 11.6 6.00 18.0 7.68 8.22 8.60 12.0 16.2 18.0 18.0Turbidity (NTU) 11 11 0% 17.7 10.3 14.5 4.10 36.0 5.20 6.30 9.20 16.0 24.5 30.0 33.0Nutrients (µg/L)Nitrogen - Nitrite, dissolved (NO 2 ) 1 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 10 2 80% 4.3 3.97 3.38 2.5 14 2.5 2.5 2.5 2.5 2.5 9.5 11.8Phosphorus, total (stream) 1 1 0% 3 NA 3 3 3 3 3 3 3 3 3 3Major Ions (mg/L)Chloride, dissolved 17 3 82% 0.312 0.362 0.246 0.150 1.70 0.150 0.150 0.150 0.250 0.250 0.300 0.580Sulfate, dissolved 17 17 0% 12.5 9.56 10.4 5.00 44.0 5.80 6.00 7.00 9.00 13.0 20.2 28.8T-128
Table 4.12. Summary <strong>of</strong> the available surface-water chemistry data for the Quesnel River Area <strong>of</strong> Interest.Life Stage/Class/AnalytennDetect% Non-DetectMeanSDGeometricMeanMinMaxPercentile Distribution5th 10th 25th 50th 75th 90th 95thMetals (µg/L)Aluminum, total 10 10 0% 194 291 92.4 7 993 17.8 28.6 47 106 180 326 660Arsenic, total 16 4 75% 0.8 1.56 0.179 0.05 5.9 0.05 0.05 0.05 0.05 0.513 2.2 3.35Boron, total 11 6 45% 289 315 60.3 5 800 5 5 5 230 535 730 765Cadmium, total 1 1 0% 0.43 NA 0.43 0.43 0.43 0.43 0.43 0.43 0.43 0.43 0.43 0.43Chromium, total 11 2 82% 0.627 0.297 0.585 0.5 1.4 0.5 0.5 0.5 0.5 0.5 1 1.2Cobalt, total 8 2 75% 0.646 0.559 0.52 0.17 2 0.286 0.401 0.5 0.5 0.5 0.95 1.48Copper, total 17 7 59% 2.09 2.41 1.17 0.5 9 0.5 0.5 0.5 0.5 3 4.7 5.8Iron, total 17 16 6% 291 348 157 2.5 1420 24.5 50.4 131 180 250 669 890Lead, total 11 0 100% 0.5 NA 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5 0.5Manganese, total 16 13 19% 15.6 12.4 11.1 2.5 41 2.5 2.5 8.25 12 20.3 34 38Molybdenum, total 17 2 88% 4.03 4.35 3.1 2.5 17 2.5 2.5 2.5 2.5 2.5 7.1 14.6Nickel, total 17 7 59% 42.5 169 1.39 0.5 700 0.5 0.5 0.5 0.5 3 4 143Selenium, total 17 2 88% 0.388 0.391 0.313 0.25 1.8 0.25 0.25 0.25 0.25 0.25 0.62 1Silver, total 11 0 100% 0.05 NA 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.05 0.05Other (µg/L)Cyanide WAD 11 0 100% 2.5 5.21E-08 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5 2.5n = 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-129
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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 4.38. 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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