Potential Effects of Contaminants on Fraser River Sockeye Salmon

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$ Water quality stations used for compliance <strong>of</strong> permitteddischarges (e.g., waste-water treatment plants, pulp and papermills, industrial discharges); and,$ Water quality stations that span key temporal periods (i.e.,pre-1990 and post-1990; 2006 and 2007).Data from a total <strong>of</strong> 142 water quality stations used in environmental impactassessments, water quality objectives development and attainment studies, trendmonitoring, discharge compliance and background characterization were compiledusing the methods listed above (Table A3.1). Spatial information (i.e., latitude andlongitude), number <strong>of</strong> samples, and length <strong>of</strong> monitoring period for each <strong>of</strong> thesestations were collated in a GIS. Of these water quality stations, a majority <strong>of</strong> thestations (identified by meeting the listed priority criteria above) were used to develop anintegrative index (CCME Water Quality Index; WQI) to characterize water qualityconditions in each <strong>of</strong> the areas <strong>of</strong> interest. The Water Quality Index (see Appendix 4)was calculated using the available water quality data and toxicity screening values(TSVs) selected from BCMOE, CCME, USEPA, or other water quality guidelinesources that are protective <strong>of</strong> any life stage <strong>of</strong> any aquatic species exposed forextended time periods.A3.4 National Pollutant Release InventoryThe National Pollutant Release Inventory (NPRI), maintained by Environment Canada,contains spatial and tabular data on the release <strong>of</strong> contaminants to air, water, and land(e.g., landfills, reclamation sites) by various industrial discharges. Industrialdischarges relevant to the assessment <strong>of</strong> sockeye salmon exposure to contaminationin the Fraser River Basin were identified in the NPRI database, including pointdischarges from the following industrial classifications:$ Agricultural industries;$ Chemical and chemical product industries;$ Crude petroleum and natural gas industries;$ Fabricated metal products industries;$ Industrial and heavy (engineering) construction industries;$ Mining industries;$ Other manufacturing industries;$ Paper and allied products industries;$ Pipeline transport industries;$ Plastic products industries;$ Refined petroleum and coal products industries;$ Transportation industries; and,$ Wood industries.A-21
A3.5 Contaminant Spill ReportsData on contaminant spills reported between March and June <strong>of</strong> 2007 in the FraserRiver Basin were compiled from Dangerous Goods Incident Reports (DGIR) providedby the B.C. Ministry <strong>of</strong> Environment. Spill type, date <strong>of</strong> spill, description and location<strong>of</strong> spill were all compiled from the Dangerous Goods Incident Reports. In addition, oilspills reported in the Fraser River were compiled from data collected by the CanadianCoast Guard.These compiled data were used to assess the potential for co-location <strong>of</strong> contaminantsand sockeye salmon during the smolt outmigration, which could affect sockeye salmonhealth and productivity <strong>of</strong> the 2009 return.A3.6 Contaminated SitesData on the location <strong>of</strong> contaminated sites in the Fraser River Basin were compiledfrom the Treasury Board <strong>of</strong> Canada=s Federal Contaminated Sites Inventory. Inaddition to geographical location, this database contains information on environmentalmedia affected (i.e., groundwater, sediment, soil, surface soil, surface water), volumeor area <strong>of</strong> contamination, the identity or types <strong>of</strong> contaminants present, last stepcompleted (e.g., initial or detailed testing program, site classification process), andclass <strong>of</strong> site (e.g., action required, action not likely required).A3.7 Metro Vancouver Sediment AssessmentIn 2006, ENKON Environmental Limited conducted a sediment monitoring program inthe Lower Fraser River for the Metro Vancouver Regional District (ENKONEnvironmental Ltd. 2007). The monitoring program was designed to meet acommitment to the District=s Liquid Waste Management Plan.Sediment data were collected at seven sites in the Lower Fraser River (downstream <strong>of</strong>McMillan Island, downstream <strong>of</strong> Barnston Island, Sapperton Channel, AnnacisChannel, Ewen Slough, Tree Island Slough, and McDonald Slough) in 2006.Parameters measured in the sediments included: conventional parameters, fecalcoliforms, total metals, PAHs (including alkylated PAHs), PCBs, organochlorinepesticides, various surfactants and plasticisers, dioxins and furans, PBDEs, andestradiols and sterols.Data were compiled from the monitoring program report and incorporated into theproject database for use in the assessment <strong>of</strong> potential effects <strong>of</strong> contaminants onFraser River sockeye salmon.A-22
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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 4.32. Frequency of</s
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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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Page 525 and 526: Figure 5.3. Fraser River Sockeye Sa
Page 527 and 528: Figure 5.5. Pitt Sockeye Salmon Pro
Page 529 and 530: Figure 5.7. Weaver Sockeye Salmon P
Page 531 and 532: Figure 5.9. Cultus Sockeye Salmon P
Page 533 and 534: Figure 5.11. Portage Sockeye Salmon
Page 535 and 536: Figure 5.13. Fennell Sockeye Salmon
Page 537 and 538: Figure 5.15. Late Shuswap Sockeye S
Page 539 and 540: Figure 5.17. Chilko Sockeye Salmon
Page 541 and 542: Figure 5.19. Early Stuart Sockeye S
Page 543 and 544: Figure 5.21. Stellako Sockeye Salmo
Page 545 and 546: Figure 5.23. Bowron Sockeye Salmon
Page 547 and 548: Appendices
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Page 555 and 556: WeaknessesThere is a lot of
Page 557 and 558: Pg 110 Ln 4189 - now called Listene
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Page 577 and 578: Appendix 4. Data Treatment and Meth
Page 579 and 580: when multiple samples were reported
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Page 585 and 586: In addition, some sockeye salmon (e
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Page 589 and 590: deBruyn, A.M., H. deBruyn, M.G. Iko
Page 591 and 592: Appendix 5. Data description and so
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Potential Effects of Contaminants on Fraser River Sockeye Salmon

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