Photo by Peter Ross..

Green/Cheakamus watersheds: Water quality report for the 2024-25 wet season

A total of 16 water samples were collected from field locations within the Green/Cheakamus watersheds on November 12, 2024 by the Raincoast Healthy Waters team alongside representatives of the Whistler Lakes Conservation Foundation. An additional 12 samples of tap water were obtained from homes and businesses in the surrounding community on the same day. A marine water sample was collected on November 13, 2024 at Porteau Cove. 

Reports

  1. 2023 dry season, DOI: 10.70766/955.423
  2. 2023/2024 wet season, DOI: 10.70766/9365.56
  3. 2024 dry season, DOI: 10.70766/4792.51
  4. 2024/2025 wet season, DOI: 10.70766/16699.1

Team

Raincoast Healthy Waters: Peter Ross, Sam Scott, and Marie Noel

Whistler Lakes Conservation Foundation: Lynn Kriwoken, Peggy English, Tom English, Katie Farley, and Addison Kits

A watershed based approach to sampling

Published on 2026 09 22.

Scott S, Kriwoken L, Noel M, and PS Ross. 2026. Green/Cheakamus watersheds: Water quality report for the 2024-25 wet season. 4 of 4. Raincoast Conservation Foundation. https://doi.org/10.70766/16699.1

Acknowledgements

We acknowledge the financial support of the Whistler Lakes Conservation Foundation. We are grateful for the enthusiastic support of Lynn Kriwoken, Peggy English, Tom English, and Lorne Kriwoken. We acknowledge the expert analytical support of Pam MacKenzie and Richard Grace at SGS-AXYS. We thank Xiangjun Liao, Andrew Ross and Neil Dangerfield at Fisheries and Oceans Canada for the provision of 6PPD-Q analysis. We thank Nicole Van Zutphen, Sherwin Arnott, and Brooke Gerle for report design. Photos by Sam Scott and Peter Ross.

Executive summary

Water is essential for life, and steps are needed to understand, protect and restore its health in fish habitat throughout British Columbia. The Raincoast Healthy Waters program was launched in 2023 to establish community-oriented water pollution monitoring in select BC watersheds. Two Healthy Waters sampling events take place every year in each watershed – the first in the dry season (summer), and the second being in the wet season (winter). 

While the Healthy Waters program typically focuses its work within singular watersheds, this partnership featured two Whistler area watersheds: the Green River, which drains through the Lillooet and Fraser Rivers into the Strait of Georgia (watershed area of 875 km2) and the Cheakamus River which drains south via the Squamish River to Howe Sound (watershed area of 1,034 km2). Combined, these watersheds cover an area of 1,909 km2. This report highlights results from the second wet (winter) season sampling carried out with the support and participation of the Whistler Lakes Conservation Foundation (WLCF). 

Briefly, the Healthy Waters – WLCF team determined basic water properties (temperature, conductivity, pH, dissolved oxygen and turbidity) in situ at sampling sites on November 12, 2024. Water samples were collected from five water categories, including source water (2 samples), stream and river water (7 samples), road runoff (6 samples), tap water (10 samples – pooled into a single composite sample) and marine water (one sample). The samples were pooled into composite by category and then analysed for coliform, nutrients (6), physical parameters, metals (37), pesticides (62), polycyclic aromatic hydrocarbons (PAHs; 76), pharmaceuticals and personal care products (PPCPs; 141), polychlorinated biphenyls (PCBs; 209), alkylphenol ethoxylates (APEs; 4), bisphenols (BPs; 6), per- and poly-fluoroalkyl substances (PFAS; 40), sucralose and 6PPD-Quinone.

We detected 113 contaminants out of 577 measured in the stream and river category – i.e. fish habitat – for the in the Green/Cheakamus watersheds, excluding nutrients, fecal coliform and physical parameters. Overall, the Green/Cheakamus watersheds had relatively good water quality in the wet season, but additional sampling and analysis will provide additional insight into contamination impacts from forest fires, domestic wastewater, industrial chemicals and road runoff on the health of this valued watershed.

The Green/Cheakamus Watershed

The water samples were collected from sites within two Whistler area watersheds: the Green River which drains northeast via the Lillooet and Fraser Rivers into the Strait of Georgia and the Cheakamus River which drains south via the Squamish River to Howe Sound. Combined, these watersheds cover an area of 1,909 km2.These watersheds are located on the traditional ancestral territories of the Sḵwx̱wú7mesh (Squamish) and Líl̓wat Nations, who have stewarded this land for millenia. Sampling sites (red stars in the upper right figure) were distributed in order to capture a range of locations for our assessment of water quality. Map by Brooke Gerle / Raincoast Conservation Foundation.
The water samples were collected from sites within two Whistler area watersheds: the Green River which drains northeast via the Lillooet and Fraser Rivers into the Strait of Georgia and the Cheakamus River which drains south via the Squamish River to Howe Sound. Combined, these watersheds cover an area of 1,909 km2.These watersheds are located on the traditional ancestral territories of the Sḵwx̱wú7mesh (Squamish) and Líl̓wat Nations, who have stewarded this land for millenia. Sampling sites (red stars in the upper right figure) were distributed in order to capture a range of locations for our assessment of water quality. Map by Brooke Gerle / Raincoast Conservation Foundation.

Key findings

  • This assessment of water quality in the Green/Cheakamus watersheds reflects the fourth of several site visits; our understanding of water quality in these watersheds will grow with additional sampling.
  • We collected composite water samples in the Green/Cheakamus River watersheds during the wet season (November 12, 2024).
  • We analysed 589 contaminants in each water sample.
  • Marine water was the most contaminated water category in the wet season; it had the highest concentrations of alkylphenols, metals, nitrate, PAHs and pesticides.
  • Stream and river water was the second most contaminated water category in the wet season; it had the highest concentration of E coli, PCBs, PPCPs and sucralose .
  • The road runoff water was third and had the highest concentrations of 6 PPD-q, bisphenols and PFAS.
  • The two source water samples (Cheakamus R. and 21 Mile Cr.) and the tap water were the least contaminated water categories in the wet season.
  • Overall, the Green/Cheakamus watersheds had relatively good water quality in the wet season:
    • There were nine exceedances of Canadian Environmental Quality Guidelines.
      • Aluminum in the Cheakamus R. sample;
      • Aluminum, copper and iron in the stream and river samples;
      • Aluminum, cadmium, copper and iron in the road runoff sample;
      • Boron in the marine sample.
    • There were no exceedances of Health Canada Drinking Water Quality Guidelines.

Background

Raincoast’s Healthy Waters Program (www.raincoast.org/waters/) delivers high-resolution, community-oriented water quality analysis to watersheds across southern British Columbia. The goal of Healthy Waters is to empower communities with the understanding of the status of water quality in their watersheds, to allow for local stewardship regarding both point and nonpoint source pollution. 

The Whistler Lakes Conservation Foundation (WLCF) studies, informs and acts to protect the waters in the Whistler area, including Alpha, Nita, Alta, Lost and Green Lakes, and their tributaries. The WLCF partnered with the Raincoast Healthy Waters team in 2023/24 to generate an analysis of contaminants of past, current and emerging concern in local waters. Water samples were collected from sites within two Whistler area watersheds: the Green River which drains northeast via the Lillooet and Fraser Rivers down into the Strait of Georgia and the Cheakamus River which drains south via the Squamish River to Howe Sound. Combined, these watersheds cover an area of 1,909 km2.

Illustration of a watershed from mountain source to urban city and sea, with icons pointing out source water, freshwater, urban runoff, tap water, and marine environment.

A watershed based approach to sampling

We collect samples from five different categories of water in each of our partner watersheds: from source water, upstream of human impacts, down to the marine environment. 

Source water serves as an upstream reference sample, allowing us to determine which contaminants are being introduced as water traces its path down through the watershed. 

Stream and river samples allow us to investigate the quality of fish habitat directly, by collecting samples from streams, creeks, and rivers used by salmon and other fish species (either currently or historically). 

Road runoff serves as an impacted sample category of current concern, as many contaminants, including  PAHs, metals, surfactants and chemicals such as 6-PPD quinone can be washed off roadways and into fish habitat during rain events. 

We include tap water samples in our analysis as a way to bring our homes into the conversation – we borrow water from the environment in the form of municipal or well water, and generally return it to aquatic habitats in a more-degraded state in the form of storm and sewage effluent (treated or untreated).

Marine water samples provide insight into those contaminants that may degrade fish and whale habitat in the ocean, and enable an understanding of the contribution of land-based pollutants from the adjacent watershed to the marine environment.

Collectively, the lessons learned from our partnering watersheds will contribute to a greater understanding of threats to water quality across British Columbia, and ultimately what policy changes can be implemented to preserve the quality of water for the future of salmon, whales, and people.

References

Berthiaume, A., Galarneau, E., & Marson, G. (2021). Polycyclic aromatic compounds (PACs) in the Canadian environment: Sources and emissions. Environmental Pollution, 269, 116008.

B.C. Ministry of Water, Land, and Resource Stewardship. 2025. 6PPD-quinone Water Quality Guidelines – Freshwater Aquatic Life. Water Quality Guideline Series, WQG-24. Prov. B.C., Victoria B.C.

CCME, 1999. Canadian Sediment Quality Guidelines for the Protection of Aquatic Life: DDT, DDE and DDD. https://ccme.ca/en/res/ddt-dde-and-ddd-canadian-sediment-quality-guidelines-for-the-protection-of-aquatic-life-en.pdf. Accessed June 2026. 

Ding, Y., Hayward, S. J., Westgate, J. N., Brown, T. N., Lei, Y. D., & Wania, F. (2023). Legacy and current-use pesticides in Western Canadian mountain air: Influence of pesticide sales, source proximity, and altitude. Atmospheric Environment, 308, 119882.

Environment and Climate Change Canada (ECCC), 2023. Update on Canada’s National Implementation plan – Under the Stockholm Convention on Persistent Organic Pollutants. https://www.canada.ca/content/dam/eccc/documents/pdf/cepa/En14-517-2023-eng.pdf.  Accessed in May 2024. 

Environment and Climate Change Canada (ECCC) and Health Canada, 2023. Draft State of Per and polyfluoroalkyl substances (PFAS). https://www.canada.ca/en/environment-climate-change/services/evaluating-existing-substances/draft-state-per-polyfluoroalkyl-substances-report.html. Accessed in May 2024. 

Government of Canada, Environment and Climate Change Canada and Health Canada, 1994. Canadian Environmental Protection Act – Priority substances list assessment report – Polycyclic Aromatic Hydrocarbons. https://www.canada.ca/content/dam/hc-sc/migration/hc-sc/ewh-semt/alt_formats/hecs-sesc/pdf/pubs/contaminants/psl1-lsp1/hydrocarb_aromat_polycycl/hydrocarbons-hydrocarbures-eng.pdf. Accessed in May 2024.

Government of Canada, 2017. Toxic substances list – hexachlorobenzene (HCB). https://www.canada.ca/en/environment-climate-change/services/management-toxic-substances/list-canadian-environmental-protection-act/hexachlorobenzene.html. Accessed in May 2024. 

Harris K.A., Dangerfield N., Woudneh M., Brown T.G., Verrin S., Ross P.S. 2008. Partitioning of current-use and legacy pesticides in salmon habitat in British Columbia, Canada. Environ Toxicol Chem 27:2253-2262.

Health Canada, 2007. Pesticides and Health. https://www.canada.ca/content/dam/hc-sc/migration/hc-sc/ewh-semt/alt_formats/hecs-sesc/pdf/pubs/contaminants/pesticides-eng.pdf. Accessed in May 2024. 

Health Canada, 2010. Polychlorinated biphenyls. https://www.canada.ca/en/health-canada/services/chemical-substances/fact-sheets/chemicals-glance/polychlorinated-biphenyls.html. Accessed in May 2024. 

Health Canada, 2011. Discontinuation of endosulfan. https://publications.gc.ca/collections/collection_2011/sc-hc/H113-5-2011-1-eng.pdf. Accessed in May 2024.

Health Canada, 2016. Special review of simazine: proposed decision for consultation. https://publications.gc.ca/collections/collection_2016/sc-hc/H113-5-2016-9-eng.pdf. Accessed in May 2024.

Marvin, C. H., Berthiaume, A., Burniston, D. A., Chibwe, L., Dove, A., Evans, M., … & Tomy, G. T. (2021). Polycyclic aromatic compounds in the Canadian Environment: Aquatic and terrestrial environments. Environmental Pollution, 285, 117442.

Morales-Caselles, C., Yunker, M.B., and Ross, P.S. 2017. Identification of spilled oil from the MV Marathassa (Vancouver, Canada 2015) using alkyl PAH isomer ratios. Archives of Environmental Contamination and Toxicology 73: 118-130.

Lo, B. P., Marlatt, V. M., Liao, X., Reger, S., Gallilee, C., Ross, A. R. S., Brown, T. M. (2023). Acute Toxicity of 6PPD-Quinone to Early Life Stage Juvenile Chinook (Oncorhynchus tshawytscha) and Coho (Oncorhynchus kisutch) Salmon. Environmental Toxicology and Chemistry, 42(4), 741-947. 

Morales-Caselles, C., Yunker, M.B., and Ross, P.S. 2017. Identification of spilled oil from the MV Marathassa (Vancouver, Canada 2015) using alkyl PAH isomer ratios. Archives of Environmental Contamination and Toxicology 73: 118-130.

Noël, M., Dangerfield, N., Hourston, R. A., Belzer, W., Shaw, P., Yunker, M. B., & Ross, P. S. (2009). Do trans-Pacific air masses deliver PBDEs to coastal British Columbia, Canada?. Environmental Pollution, 157(12), 3404-3412.

Othman, N., Ismail, Z., Selamat, M. I., Sheikh Abdul Kadir, S. H., & Shibraumalisi, N. A. (2022). A review of polychlorinated biphenyls (PCBs) pollution in the air: where and how much are we exposed to? International Journal of Environmental Research and Public Health, 19(21), 13923.

Ross, P. S., Ellis, G. M., Ikonomou, M. G., Barrett-Lennard, L. G., & Addison, R. F. (2000). High PCB concentrations in free-ranging Pacific killer whales, Orcinus orca: effects of age, sex and dietary preference. Marine Pollution Bulletin, 40(6), 504-515. https://doi.org/10.1016/S0025-326X(99)00233-7 

Schulz, R. (2004). Field studies on exposure, effects, and risk mitigation of aquatic nonpoint‐source insecticide pollution: A review. Journal of environmental quality, 33(2), 419-448. https://doi.org/10.2134/jeq2004.4190 

Tian et al. (2021). A ubiquitous tire rubber–derived chemical induces acute mortality in coho salmon. Science 371,185-189. DOI:10.1126/science.abd6951

UNEP. 2025. United Nations Environment Programme: Stockholm Convention on Persistent Organic Pollutants. Accessed June 2025: https://www.pops.int/partners/unep/overview/tabid/255/default.aspx 

van Elsas, J.D., Semenov, A.V., Costa, R., Trevors, J.T. Survival of Escherichia coli in the environment: fundamental and public health aspects, The ISME Journal, Volume 5, Issue 2, February 2011, Pages 173–183, https://doi.org/10.1038/ismej.2010.80

van Stempvoort, D.L., Brown, S.J. Spoelstra, J., Garda, D., Robertson, W.D., and Smyth, S.A.. 2020. Variable persistence of artificial sweeteners during wastewater treatment: Implications for future use as tracers. Water Research 184: 116124. https://doi.org/10.1016/j.watres.2020.116124.