Introduction to the Crown-Indigenous Working Group for the Potential Oil Sands Mining Effluent Regulations

1. Introduction

1.1. Disclaimer

The members of the Crown-Indigenous Working Group (CIWG) for the Potential Oil Sands Mining Effluent Regulations participate in good faith in support of the Government of Canada’s commitment to renewed Nation-to-Nation and government-to-government relationships that are based on recognition of rights, respect, collaboration, and partnership as the foundation for transformative change. Participation by the First Nations, Métis Nations and Métis communities in the CIWG should not be interpreted as tacit support or acceptance of oil sands mine water release or as an abrogation or derogation of their rights. This document was developed collaboratively by CIWG members. While CIWG members support this document in principle, some statements may not fully represent the position of each member.

1.2. Purpose

As the Government of Canada’s lead department for the protection and conservation of the environment, Environment and Climate Change Canada (ECCC) is exploring options to manage oil sands mine water on the sites of surface mines located in the Lower Athabasca Region in Northern Alberta. The CIWG has prepared this introductory paper to provide interested parties with an update on the work completed by the CIWG to date, an overview of the collaborative process established through the CIWG, and an opportunity for early feedback. This paper was developed collaboratively by the CIWG. This paper will be followed by several planned engagement documents and marks the start of several planned public consultation periods. Any interested parties may comment in writing by e-mail or mail.

2. Context

2.1. The Crown-Indigenous Working Group

The CIWG was established in January 2021 in response to concerns raised by Indigenous communities regarding potential releases of oil sands mining effluent to the Athabasca River watershed. It is meant to serve as a mechanism for collaboration to assess whether regulations authorizing releases of treated oil sands mining effluent are needed, and if necessary on the development of potential regulations for oil sands mining effluent. The CIWG is composed of representatives from ECCC and nine Indigenous communities located in and downstream of the oil sands area includingFootnote 1 :

The work of the CIWG includes identifying issues, developing analyses and issue papers, conducting and/or reviewing research, and co-drafting engagement documents. Should ECCC continue developing potential regulations for oil sands mine water release, the CIWG will be involved in the regulatory development process.

In order to determine whether regulations authorizing the release of oil sands mining effluent are necessary and justified, the CIWG is currently working on an assessment of alternative options to the release of treated mine water. At the same time, the CIWG is continuing the technical and scientific research and analyses needed to establish potential regulations, in the event it is determined that authorizing release is necessary and justified.

Regulations, if established, will be protective of the environment and the human health of Indigenous people and consistent with the Crown’s obligations to Indigenous peoples.

2.2. Treaty and Aboriginal rights

The Government of Canada is committed to reconciliation with Indigenous Peoples through a renewed, nation-to-nation and government-to-government relationship, based on the recognition of rights, respect, collaboration, and partnership. Consideration of options to manage the accumulation of oil sands process-affected water in the existing tailings ponds includes potential regulations allowing for the release of treated oil sands mining effluent. Such a regulation or other management options requires careful assessments of potential impacts to Treaty and Aboriginal rights guaranteed by Section 35 of the Constitution Act (1982) and the health and well-being of Indigenous people. It also requires consideration of commitments made by the Government of Canada under the United Nations Declaration of the Rights of Indigenous Peoples ActFootnote 2 as well as the findings and recommendations of the Report of the Royal Commission on Aboriginal Peoples and Truth and Reconciliation Commission of Canada: Calls to Action. The release of oil sands mining effluent would occur in a context in which Indigenous communities in and downstream of the oil sands region have already experienced significant, cumulative impacts to their rights and health.

The oil sands mining area is located within the territory of Treaty 8, which encompasses a landmass of approximately 840,000 square kilometres and is home to 39 First Nations communities. Treaties, including Treaty 8, define ongoing rights and obligations between Indigenous Peoples and the Government of Canada. Honouring treaties is essential for Indigenous and non-Indigenous peoples to live together in Canada. Likewise, for Sovereign Métis Nations where no treaties are signed by independent Métis Powley communities, discussions on Aboriginal Title with Canada are still ongoing and thus, are considered in this regulatory development process. Indigenous communities assert that their rights in relation to the river have not been ceded or modified and that the Crown has a duty to obtain consent prior to authorizing any releases to the river.

ECCC is committed to ensuring that impacts to treaty and Aboriginal rights resulting from the potential release of oil sands mining effluent are understood and fully considered. If it is determined that there are no appropriate alternatives to regulations authorizing the release of treated oil sands mining effluent and that they are necessary, ECCC will work with impacted parties to assess potential impacts to rights. The results of those assessments will inform decisions on what is needed to avoid and mitigate impacts to rights and, if impacts cannot be avoided or mitigated, to inform discussions of accommodation measures and free, prior and informed consent. Indigenous people in the region have significant concerns about the potential for adverse effects to the health and populations of fish and aquatic species and to human health from water and aquatic resource consumption and use, which is an integral part of their section 35 rights, including the ability to preserve and transmit Indigenous knowledge

In parallel to the CIWG, Indigenous communities and ECCC will work together bilaterally to assess the potential impacts to treaty or Aboriginal rights resulting from options to manage the accumulation of oil sands process-affected water in the tailings ponds, including potential regulations allowing for the release of treated oil sands mining effluent. Indigenous community members of the CIWG and ECCC are currently working together to develop frameworks for the rights impact assessment process. This work is still in its early stages but will be essential if regulations allowing for the release of oil sands mining effluent are to be developed. ECCC is also committed to working with Indigenous communities outside of the CIWG that may experience impacts to their environment and/or Aboriginal and treaty rights.

2.3. Oil sands mining sector

Mining of oil sands to extract bitumen has been undertaken on a commercial scale for over 50 years. Oil sands mining involves first exposing the ore by removing overburden and muskeg. The oil sands ore is then mined and transported to crushers to be broken into smaller pieces. A slurry containing the mined ore and hot water is formed and sent to separation cells that use gravity to isolate the bitumen from the coarse solids (mostly silica sand). This step generates a froth that requires further treatment using a solvent or diluent to reduce the viscosity and allow for further gravity separation of any remaining water and fine solids. Extracted bitumen is then sent to either an upgrader or a high-conversion refinery. Upgraders turn extracted bitumen into synthetic crude oil, which is then sent to a refinery to be made into petroleum products that are sold to end users; high-conversion refineries are capable of processing bitumen without the intermediary step of upgrading.

The oil sands mining processes require large amounts of water. The bitumen extraction process generates mine water and tailings that are stored in tailings ponds. Approximately 12-15 barrels of tailings are generated for each barrel of bitumen produced. Despite high rates of water recycling, tailings ponds continue to grow. There are approximately 28 tailings ponds in the oil sands region spanning over 220 km2. In 2021, the Alberta Energy Regulator reported 8 operating oil sands mines storing approximately 1.3 billion m3 of fluid tailings (enough to fill about 540,000 Olympic-sized swimming pools) and 472 million m3 of tailings water in 28 tailings impoundment structures (that is, tailings ponds) (Figure 1, 2)Footnote 3 .

Figure 1 Operating and approved oil sands mining projects and tailings pond/deposits in 2021. Alberta Energy Regulator 2022.
Long description

This map of northeastern Alberta shows current, proposed, and planned oil sands mining projects as of 2021. Current oil sands mining projects have pink labels. Proposed oil sands mining projects have yellow labels. Planned oil sands mining projects have green labels. Black labels identify the locations of tailings ponds or storage facilities across the map.

A grid of the Alberta Township System is overlaid on the map. The map shows Townships 102 to 90 and Ranges 4 to 13 West of the 4th Meridian. Areas occupied by oil sands projects are labelled with pink horizontal lines.

A legend in the bottom-right corner of the map states that “the AER does not warrant the accuracy or completeness of the information contained in this map and is not responsible for any errors or omissions in its content and accepts no liability for the use of this information.” Below the map, there is a small-print that states “base data contains information licensed under the Open Government License – Alberta”.

The oil sands mining projects are separated into three distinct areas on the map. Teck Frontier occupies the northern-most area on the map and has a yellow label. This project has since been terminated as of 2020.

South of the Teck Frontier site is a large grouping of oil sands projects. Moving from West to East, this grouping includes:

  • CNRL Horizon North and South
  • Fort Hills
  • Syncrude Aurora North
  • CNUL Muskeg River
  • CNUL Jackpine and Jackpine Expansion
  • Imperial Kearl and
  • Syncrude Aurora South

All these projects have pink labels, except for Syncrude Aurora North, which has a green label.

The Suncor Mildred Lake and Millennium oil sands mines are situated just South of the grouping. All Suncor sites have pink labels. Labelled in black, there are:

  • 1 tailings storage facility West of CNRL Horizon
  • 14 tailings storage facilities distributed between Fort Hills, Aurora North, Muskeg River and Jackpine,
  • 4 tailings storage facilities North of Imperial Kearl
  • and 20 tailings storage facilities distributed between Syncrude Mildred lake, Suncor Base Mine and Millennium
Figure 2 Ponded water volume in tailings ponds, 2014 to 2021. Water volumes are presented as reported by operators and are subject to change upon further review by the AER. Source: State of Fluid Tailings Management for Mineable Oil Sands, 2021. Alberta Energy Regulator. October 2022. Note that this only represents water in the clear water zone of tailings ponds. There is also water held in fluid tailings and solid waste (not included), which will be released to the clear water zone as the tailings consolidate.
Long description

This vertical stacked bar chart presents the total volume of water in tailings ponds annually from 2014 to 2021. Vertical bars for each year are striped by four shades of green and four shades of blue indicating different mine sites.

Each company is represented by a colour and placement in the bars. From top to bottom, they are:

  • Suncor Fort Hills is represented by dark green. It is only present in the graph for the years ranging from 2018 to 2021
  • Imperial Kearl is represented by tan green
  • CNRL Horizon is represented by light green
  • CNUL Jackpine Mine is represented by vivid green
  • CNUL Muskeg River Mine is represented by vivid blue
  • Suncor Base Plant is represented by light blue and has larger bars for ponded water
  • Syncrude Aurora North is represented by grey blue
  • Syncrude Mildred Lake is represented by dark blue and has the largest bars across all years

Below the graph a figure caption reads:

“Figure 2 Ponded water volume in tailings ponds, 2014 to 2021. Water volumes are presented as reported by operators and are subject to change upon further review by the AER. Source: State of Fluid Tailings Management for Mineable Oil Sands, 2021. Alberta Energy Regulator. October 2022. Note that this only represents water in the clear water zone of tailings ponds. There is also water held in fluid tailings and solid waste (not included), which will be released to the clear water zone as the tailings consolidate.”

The numerical data indicated by the bar graph is as follows, in million meters cubed volumes:

Oil Sands Project

2014

2015

2016

2017

2018

2019

2020

2021

Suncor Fort Hills

0

0

0

0

3.0

5.7

12.7

16.6

Imperial Kearl

21.3

27.7

19.9

19.7

18.7

22.7

26.8

17.0

CNRL Horizon

33.0

30.0

33.0

28.2

31.1

31.1

30.0

25.2

CNUL Jackpine Mine

19.8

15.0

10.8

12.2

16.0

19.8

18.4

22.7

CNUL Muskeg River Mine

9.8

8.9

13.3

16.3

20.6

20.4

22.5

27.9

Suncor Base Plant

126.2

106.3

119.3

111.4

118.0

104.6

106.4

108.6

Syncrude Aurora North

71.8

75.5

68.0

60.9

75.4

78.3

93.1

97.1

Syncrude Mildred Lake

126.5

138.2

137.4

144.1

147.5

155.9

169.4

156.6

2.4. Regulatory context

Oil sands mining operations must comply with all applicable federal legislation, including the Fisheries Act. The Minister of the Environment and Climate Change is responsible for the administration and enforcement of the pollution prevention provisions of the Fisheries Act. Subsection 36(3) of the Fisheries Act prohibits anyone from depositing or permitting the deposit of a deleterious substance in water frequented by fish, or in any place where the deleterious substance may enter such water. The Fisheries Act allows for the establishment of federal regulations that could authorize the discharge of deleterious substances under conditions set out in the regulations. There are currently no regulations authorizing the release of oil sands mining effluent. Instead, oil sands mines retain most of the water used in their processes including site runoff, waters used during extraction, significant amounts of water from depressurization and removal of waters as mining occurs and progresses, and significant amounts of accumulated precipitation, since they began operating. Waters of variable composition and toxicity are mixed and moved around, ultimately being stored in large and multiple ponds.

The release of oil sands mine water is not authorized by provincial regulations or project-specific approvals. The Government of Alberta is developing provincial regulatory requirements for releases of oil sands mine water. ECCC and Alberta Environment and Protected Areas (AEPA), are engaging regularly to share information and coordinate activities where appropriate. The CIWG is not involved in this engagement between ECCC and AEPA.

3. Considerations

3.1. Substances of concern

Oil sands mining produces several by-products or waste streams from both the processing of oil sands to extract bitumen and the physical disturbance of surface and groundwater required to extract the oil sands. The variety of liquid wastes produced by oil sands mining, and the manner in which they are managed, combined and accumulated over significant periods of time, makes identifying oil sands mine water challenging. Sources of oil sands mine water that could contribute to mining effluent include:

Oil sands mine water has unique physical and chemical qualities. It contains elevated concentrations of several compounds of concern known to be toxic to organismsFootnote 4 . Chemical concentrations vary between tailings ponds due to differences in ore composition, extraction processes, and pond age. The following chemical classes and types have been identified in tailings water and fine sediments (Table 1)Footnote 5 .

Table 1. Classes and types of chemicals identified in tailings pond water and fine sediments.

Chloride and other inorganic salts

Ammonia

Sulphate and sulfides

Phenols

Cyanide

Polycyclic Aromatic Hydrocarbons (PAHs)

Volatile Organic Compounds (VOCs; including benzene, toluene, ethylbenzene, xylene (BTEX))

Petroleum Hydrocarbons (PHCs) Fractions (F)1-4 and oil and grease

Naphthenic Acids (NAs; acid extractable)

Total Dissolved Solids (TDS)

Heavy metals

Trace elements

Nitrates and nitrites

Phosphorous and other nutrients

Flocculants and coagulants

-

3.1.1. Discussion questions

Are there additional substances of concern in oil sands mine water of which the CIWG should be aware or should consider? If so, what are they, and why are they of concern?

3.2. Information gaps

The end goal of oil sands mine closure is to reclaim disturbed lands to a functioning ecosystem that is integrated with the surrounding environment. Oil sands mine operators assert that releases of treated effluent are needed to address the accumulation of oil sands process water over time and to facilitate mine closure and reclamation. The need for releases of treated effluent was not previously contemplated in the near term and quantification has not occurred that demonstrates how releases of treated effluent will achieve these outcomes while protecting the environment, human health and Aboriginal and treaty rights. The CIWG is currently assessing the magnitude of fluid accumulation. In addition, more information is needed on the nature of oil sands mine water that might be released from oil sands mining operations. It is critical to understand which waters (type, composition, toxicity) are being considered for release, where and how much would be released, and the frequency and timing of potential releases across the sector.

3.2.1. Discussion questions

Are there any sources of information or resources on the magnitude of fluid accumulation or the nature of oil sands mine water that the CIWG should be aware? If so, what are they and why are they relevant to this process?

3.3 Alternatives to Releases of Treated Oil Sands Mine Water

The CIWG is currently assessing alternative options to the release of treated oil sands mine waters, such as increased water recycling, local and regional reuse of waters, segregation and targeted treatment of waters based on source of production and quality to increase reuse and recycle, and alternative disposal options. Given the volumes involved, the varied composition, and uncertainties associated with these waters, an integrated approach that considers alternatives is needed before releases of oil sands mining effluent can be authorized.

3.3.1. Discussion questions

Are there additional alternatives to regulations that CIWG should consider? If so, what are they and why do you think they should be considered?

3.4. Cumulative Impacts

Existing oil sands tailings are located in close proximity to the Athabasca River (Figure 1). The Athabasca River watershed is already experiencing cumulative effects from oil sands, urban, industrial, and agricultural developmentFootnote 6 . Release of oil sands mine water will have additive impacts to these existing impacts that must be considered and assessed. The number and size of oil sands tailings will also result in multiple releases from multiple operations within a short distance of the Athabasca River. The cumulative effects of these multiple releases must also be fully assessed and considered.

The Athabasca River empties into the Peace Athabasca Delta, which is the world's largest inland, freshwater delta and is within Wood Buffalo National Park, a UNESCO World Heritage Site. The Delta then feeds the Slave River and the Slave Delta. In addition to water quality loads, the sediment impact of oil sands mine water release to these deltaic environments receive large volumes of sediments.

In addition to the potential for cumulative impacts described above, there are many existing authorized discharges of effluent to the Athabasca River and its tributaries that must be considered in the status and health of the aquatic ecosystems in the region. How these releases in combination with climate change, land use change, and future development may cumulatively impact the region must also be considered in the development of a regulation for release of treated oil sands mining effluent.

4. Ongoing and Planned Work

4.1. Ongoing Work

The following is a list of work items currently being completed by the CIWG:

4.1.1. Discussion questions

Is there existing research or information that the CIWG should consider in support of these work items? If so, what is it?

4.2. Planned Work

The following is a preliminary list of work items the CIWG plans to conduct in support of development of potential regulations for oil sands mining effluent. This work is subject to the results of the assessment of alternatives to the treatment and release of oil sands mining effluent, which will help determine whether regulations authorizing release are needed. This list is not exhaustive and does not preclude the CIWG from conducting any additional work it deems necessary.

4.2.1 Discussion questions

Are there any additional assessments the CIWG should consider? If so, what are they and why should they be considered?

5. Timelines and next steps

5.1. Public consultation process

The CIWG plans to release engagement documents, followed by targeted consultation sessions, at regular intervals throughout regulatory development. The frequency and timing of these papers and information sessions will be determined by the results of the assessment of alternatives and feedback from the consultation sessions.

5.2. Timelines

The publication of this paper will be followed by engagement sessions with interested parties. Interested parties are welcome to provide written feedback on the paper by September 15,2023 .

If it is determined that regulations authorizing the release of treated oil sands mining effluent are needed, ECCC is committed to taking the time necessary to meaningfully consult with Indigenous communities.

6. References

AER. 2022. State of Fluid Tailings Management for Mineable Oil Sands, 2021.

Allen, E.W., 2008. Process water treatment in Canada’s oil sands industry: I. Target pollutants and treatment objectives. Journal of Environmental Engineering and Science, 7(2), pp.123-138.

Canadian Council of Ministers of the Environment (CCME). Canadian Environmental Quality Guidelines (CEQGs). Undated. Accessible at: Canadian Council of Ministers of the Environment | Le Conseil canadien des ministres de l'environment (ccme.ca)

Mahaffey, A. and Dubé, M., 2017. Review of the composition and toxicity of oil sands process-affected water. Environmental Reviews, 25(1), pp.97-114.

Government of Alberta. 2018. Environmental Quality Guidelines for Alberta Surface Waters. Water Policy Branch, Alberta Environment and Parks. Edmonton, Alberta

US EPA. 2015. National Recommended Water Quality Criteria - Human Health Criteria Table. Accessible at: National Recommended Water Quality Criteria - Human Health Criteria Table | US EPA

Health Canada. 2021. Guidelines for Canadian drinking water quality—summary table. Accessible at: Canadian Drinking Water Guidelines - Canada.ca

Tondu, J.M.E., 2017. Longitudinal water quality patterns in the Athabasca River: winter synoptic survey (2015). Alberta Environment and Parks.

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