Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Table A3.1. Water quality stations used in the assessment <strong>of</strong> potential effects <strong>of</strong> contaminantson sockeye salmon.EnvironmentalMonitoringSystem StationSamplingStart DateSamplingEnd DateSockeye Salmon Habitat Use Latitude LongitudeSouth Thompson River Area <strong>of</strong> Interest (continued)0600135 18-Oct-73 01-Mar-10 Upstream and Outmigration 50.6794 -120.32330500293 23-Oct-73 10-Aug-10 Spawning 50.2525 -118.96030500462 29-Jul-75 25-Aug-98 Spawning 50.9379 -118.43150500463 29-Jul-75 05-Oct-94 Spawning 50.9417 -118.48220500498 08-Jan-76 29-Nov-90 Upstream and Outmigration 50.5634 -119.13940500497 08-Jan-76 27-Feb-91 Upstream and Outmigration 50.5639 -119.13670500697 01-Mar-79 15-Apr-09 Spawning 50.2886 -118.92420500686 15-Mar-79 04-Aug-94 Spawning 50.9342 -118.4447E206092 23-Jan-85 03-Aug-10 Spawning 50.6929 -119.3298E206084 23-Jan-85 18-Mar-10 Spawning 50.2844 -119.985E206087 23-Jan-85 18-Mar-10 Spawning 50.4892 -119.6E206086 23-Jan-85 18-Mar-10 Spawning 50.4078 -119.8119E206089 26-Feb-85 22-Sep-10 Spawning 50.4561 -119.3728E206246 11-Apr-85 22-Sep-10 Spawning 50.9475 -118.7708E206771 03-Sep-86 21-Jul-10 Spawning; Rearing 50.7239 -119.3014E206964 21-May-87 15-Dec-87 Spawning; Rearing 51.2578 -118.9483E207579 27-Jul-88 18-Mar-08 Spawning; Rearing 50.7634 -119.2223E208719 30-May-90 28-Sep-04 Spawning; Rearing 51.0022 -119.0177E208721 30-May-90 23-Sep-10 Spawning; Rearing 51.0686 -118.917E208722 31-May-90 17-Aug-10 Spawning; Rearing 51.1301 -119.0089E208734 19-Jul-90 17-Mar-10 Spawning; Rearing 50.8805 -119.4623E222131 13-Sep-95 17-Mar-10 Spawning; Rearing 50.9582 -119.1044E227530 06-Aug-97 22-Aug-07 Spawning; Rearing 50.9756 -119.1149E233390 16-Aug-98 07-Oct-02 Spawning 50.5848 -119.3764E263504 18-May-10 21-Jul-10 Spawning; Rearing 50.7094 -119.2941E263503 18-May-10 21-Jul-10 Spawning; Rearing 50.7094 -119.2941E282475 06-Jul-10 06-Jul-10 Spawning; Rearing 50.9124 -119.5254E282479 06-Jul-10 06-Jul-10 Spawning; Rearing 50.8794 -119.3709E282484 06-Jul-10 06-Jul-10 Spawning; Rearing 50.9686 -119.0791E282477 06-Jul-10 06-Jul-10 Spawning; Rearing 50.7982 -119.1136E282485 06-Jul-10 06-Jul-10 Spawning; Rearing 50.936 -119.245E282481 07-Jul-10 07-Jul-10 Spawning; Rearing 50.7928 -119.0815E282480 07-Jul-10 07-Jul-10 Rearing 50.7794 -119.3104Upper Fraser River Area <strong>of</strong> Interest River0600011 01-May-72 16-Aug-10 Upstream and Outmigration 52.53 -122.44250400023 17-May-72 18-Mar-97 Upstream and Outmigration 54.0761 -121.8458E206182 05-Mar-85 03-May-05 Upstream and Outmigration 53.6383 -122.6644ReferenceE236796 28-Jul-84 19-Jul-10 N/A 52.9881 -119.0092A-29
Appendix 4. Data Treatment and MethodologyA4.1 Treatment <strong>of</strong> Spatial DataSpatial data were obtained from multiple sources in various formats. To standardizethe spatial data into a consistent format, data were converted into ESRI7 shapefilesand projected using the North American Datum (NAD) 1983 BC Environment Alberscoordinate system. Due to the lack <strong>of</strong> data availability and, in some cases, difficultyacquiring spatial data, a variety <strong>of</strong> data mining and data creation techniques wereimplemented. This included, but was not limited to, using Google Earth to generategeographic representations, geo-referencing figures from existing reports, and plottingfacilities and land-use activities from coordinates presented in tabular data. In somecircumstances, only the mailing address <strong>of</strong> the facility was available. In this situation,Google Earth was utilized to obtain the spatial coordinates <strong>of</strong> the facility andsubsequently plotted in ESRI7 ArcMapJ.Many <strong>of</strong> the spatial datasets required formatting and conversion in order to accuratelyand efficiently use the data, information, and maps. Sources <strong>of</strong> spatial data includedscientific and grey-literature, published reports, Micros<strong>of</strong>t Access databases, Micros<strong>of</strong>tExcel spreadsheets, ESRI7 ArcMapJ shapefiles, online mapping tools, and textdescriptions. Spatial datasets, which required unique handling, are described below.RESULTS-Openings Spatial DatabaseThe RESULTS-Openings spatial database was acquired through GeoBC=s DataDiscovery Service and was used to identify predominant tree species and tosummarize and display harvesting activities within the Fraser River Basin in thefollowing time periods: APre-1990" (1960-1990 inclusive) and APost-1990".To achieve these results, the polygons provided in the RESULTS-Openings databasewere overlaid and intersected with the area <strong>of</strong> interest boundaries to extract therelevant information. Micros<strong>of</strong>t Access was then used to classify the data into theAPre-1990" and APost-1990" time periods. In order to do this, the DN1_CompDate (thefirst disturbance completion date) and DN2_CompDate (the second disturbancecompletion date) fields were used in several queries. To achieve the desired results,the following rules were used:$ All DN1_CompDate years falling between 1960 and 1990(inclusive) were classified as APre-1990".$ All DN1_CompDate years occurring after 1990 were classified asAPost-1990".$ All DN2_CompDate years falling between 1960 and 1990(inclusive) where DN1_CompDate field was blank were classifiedas APre-1990".A-30
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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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Figures
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Figure 5.1. Water Quality Index sco
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
Page 549 and 550: SW4 Deliverables4.1 The Contractor
Page 551 and 552: obtained on one species, sometimes
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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 567 and 568: 4. Keyword searches for water quali
Page 569 and 570: A3.5 Contaminant Spill ReportsData
Page 571 and 572: River Pulp, Kamloops Cellulose Fibr
Page 573 and 574: Table A3.1. Water quality stations
Page 575: Table A3.1. Water quality stations
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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