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Advancing a Circular Energy Economy for Bitcoin Mining in Canada

Provincial energy policy and enforceable circularity conditions

Contents

Bitcoin mining energy estimates are live model outputs rather than settled facts. Cambridge CBECI provides a daily power-demand estimate and an annualised electricity-consumption estimate; any circulated version must archive the value used. Canada's provincial electricity systems differ sharply in generation mix and regulatory posture, producing widely different outcomes from the same mining load. Quebec runs on hydroelectric power but has moved toward tighter blockchain-specific pricing. Alberta remains more permissive and more carbon-intensive. The analysis covers four provincial frameworks and argues that mining contributes to circular economy objectives only under enforceable conditions: contractual interruptibility, audited heat recovery, and binding carbon-intensity standards.

I. Introduction

Canada has accounted for a material historical share of global Bitcoin mining activity. The Cambridge Centre for Alternative Finance estimated Canada’s contribution at roughly 6 to 10 percent of global network hashrate in the 2021 to 2022 period, though precise shares fluctuate with mining pool reporting and seasonal hydroelectric availability [1]. Between 2021 and 2022, Canadian mining operations consumed several terawatt-hours of electricity per year, placing Canada approximately sixth globally in mining-related energy usage [2].

Canada’s electricity generation mix provides a structural advantage in the historical estimate used here. Canada’s electricity supply is approximately 60 percent hydroelectric [2], so mining-related CO2 emissions from Canadian operations were proportionally lower than in fossil-dependent jurisdictions during the 2021 to 2022 study window. Canadian Bitcoin mining accordingly accounts for only a small fraction of national greenhouse gas emissions.

These national averages, however, obscure the provincial variation that defines Canadian energy policy. The same 100 MW mining load produces radically different climate, grid, and economic outcomes depending on whether it connects in Quebec, British Columbia, Alberta, or Manitoba. This divergence is the central policy problem.

CBECI
Primary live energy estimate
6–10%
Canada hashrate share, 2021-2022 estimate
~60%
Canadian mining from hydro, study-period estimate
~0.1%
Mining share of Canada GHG emissions, study-period estimate
Sources: Geophysical Research Letters (2023) · Cambridge CBECI methodology · Environment and Climate Change Canada

Where the physical grid is indifferent to the use of energy, the policy framework introduces the distinction that determines whether a watt functions as waste or resource, as extraction or contribution to circular systems.

Globally, Bitcoin mining energy consumption is best treated as a live estimate. Cambridge CBECI provides the primary source here because it reports daily power demand and annualised electricity consumption under an explicit lower-bound, best-guess, and upper-bound model [18]. Secondary statistics sites report higher late-2025 figures, but those figures should not carry the headline claim without archived methodology and same-day corroboration. The historical comparison remains useful: mining was estimated at approximately 173 TWh for 2020 to 2021 [2]. Global mining-related CO2 estimates require date-stamped refresh because hardware efficiency, hashrate, electricity mix, and renewable share continue to move.

The April 2024 Bitcoin halving, which reduced the block subsidy from 6.25 to 3.125 BTC, has intensified competitive pressure on miners. Operators with higher electricity costs or less efficient hardware face tighter margins, accelerating migration toward jurisdictions with cheap power and concentrating the industry among larger, better-capitalized operations. This structural shift compounds the policy stakes for Canadian provinces: the miners arriving are larger, more energy-intensive, and more strategically responsive to regulatory asymmetry than the cohort of 2020 to 2022.

II. Provincial Policy Framework Analysis

Quebec: Controlled Integration and Circular Economy Incentives

Quebec attracts cryptocurrency miners through abundant hydroelectricity and globally competitive electricity rates. By 2019, Hydro-Quebec had approved approximately 368 MW of crypto mining load and allocated an additional 300 MW block through a competitive process [3] [4]. Earlier demand had already pushed Quebec into a formal selection process for blockchain electricity use [7].

Quebec’s regulatory architecture has three structural features:

First, a competitive allocation process requiring mining companies to bid for electricity access. Proposals are evaluated on local economic benefits, job creation, and energy reuse potential. Waste heat recovery received a 10 percent weighting in project assessments, explicitly incentivizing circular economy practices [4].

Second, interruptible power contracts requiring miners to reduce consumption during peak winter demand. This limits electricity use by miners for up to 300 peak-demand hours per year [5], preserving grid stability for residential and industrial customers.

Third, a dedicated mining tariff ("Rate CB") applies to medium- or large-power contracts where at least 50 kW is dedicated to cryptographic use applied to blockchains. Hydro-Quebec’s customer page captured in the May 17 source packet flags a rate increase effective April 1, 2026, and its February 2026 filing posture proposes a revised blockchain rate averaging 19.5¢/kWh for the second half of 2026, subject to Regie de l’energie approval [20] [6]. The policy direction in the captured materials is clear even where the final tariff status remains live: blockchain load is being priced as an energy-intensive use with limited economic benefit.

These combined measures limited uncontrolled expansion. Quebec’s strict approach also deterred investment: the 2019 call for proposals later produced only 32.6 MW in pre-project agreements out of the 300 MW block [7]. Many miners established operations in provinces with less restrictive conditions.

Assessment. Quebec’s framework is the most institutionally coherent among Canadian provinces. Its weakness is static calibration: evaluation weights and tariff levels set at inception have not been systematically updated against measured outcomes. A dynamic recalibration mechanism, periodically adjusting scoring weights based on observed curtailment compliance, delivered heat volumes, and local economic contribution, would improve long-term effectiveness while preserving capacity control.

British Columbia: From Moratorium to Effective Ban

British Columbia offers desirable mining conditions: renewable sources generate over 98 percent of the province’s electricity [8]. By late 2022, BC Hydro had received 21 project proposals totalling 11,700 GWh per year (11.7 TWh) of additional mining load, equivalent to more than two Site C dams' annual generation and to roughly 1,400 MW of continuous load [8].

The provincial government imposed an 18-month moratorium on new mining connections in December 2022, suspending all pending proposals to prioritize electricity availability for transportation electrification, industrial decarbonization, and residential heating [8].

During the moratorium, British Columbia passed Bill 24 (Energy Statutes Amendment Act, 2024), granting authority to restrict, regulate, or conditionally approve future electricity connections specifically for crypto mining [9]. The legislation enables regulations that can prohibit utilities from supplying electricity to miners for specified or indefinite periods, set capacity limits, and establish conditions for service provision.

Regulatory update. By October 2025, BC moved from moratorium to prohibition for new BC Hydro mining connections. The provincial government announced a permanent ban on new BC Hydro connections for cryptocurrency mining, and the Cryptocurrency Power Regulation captured in the May 17 source packet prohibits the authority from supplying service to new low-voltage and high-voltage cryptocurrency projects, including by accepting design deposits or entering system-impact and facilities-study agreements [31] [32]. This represents a significant escalation from conditional regulation to legal exclusion.

British Columbia’s single operational demonstration of circular potential remains the MintGreen project in North Vancouver. According to company-facing public materials and reporting, MintGreen’s "Digital Boilers" use immersion technology to recover more than 96 percent of the electricity consumed by mining as usable heat, delivered through Lonsdale Energy Corporation’s district heating system to approximately 100 residential and commercial buildings [10] [21]. The 20,000-tonne emissions figure is treated here as company-reported project evidence rather than an independently verified annual per-megawatt yield. Scenario B projections of 30-40% national heat recovery therefore operate as a sensitivity case built from a proof-of-concept rather than as an established scalability finding.

Assessment. BC’s trajectory illustrates the political economy of mining regulation. When the planning system cannot absorb demand at the scale proposed, and when the perceived employment-to-energy ratio is unfavourable, the policy response escalates from conditional management to exclusion. The MintGreen project shows that mining can deliver measurable circular value through documented heat recovery, but a single pilot was insufficient to change the province’s trajectory.

Alberta: Market Flexibility with Structural Carbon Exposure

Alberta operates a permissive, market-oriented approach. Its deregulated electricity market imposes few restrictions on mining operations. Miners contract power through private agreements or develop their own generation sources. Cheap natural gas, abundant fossil fuels, and readily available flared gas from oil production attract mining investment [11].

Alberta’s market structure incentivizes voluntary curtailment when electricity prices rise, providing short-term grid flexibility without formal mandate [1] [14]. Voluntary behaviour is not equivalent to dispatchable contracted demand response; miners face no mandated requirements for load curtailment or responsible grid behaviour.

The primary challenge is carbon intensity. Alberta’s electricity sector has undergone significant change in the CER profile captured in the May 17 source packet: emissions decreased 60 percent from 2005 to 2023, with a 53.6 percent decline between 2015 and 2023 alone. The province completed its coal-to-gas transition in June 2024, and renewable energy (wind, solar, hydro) contributed approximately 19 percent of total generation in 2024, up from 17 percent in 2023 [12].

Despite this progress, Alberta’s grid remains substantially more carbon-intensive than Quebec’s or BC’s hydro-dominant systems. A typical 1 MW mining facility in Alberta generates approximately 5,300 tonnes of CO2 annually [12] based on 2023 grid-intensity baselines. With Alberta’s coal-to-gas transition completing in June 2024, this figure now overstates present emissions, which continue declining with the grid transition while remaining substantially higher than equivalent operations on hydro-dominant grids.

Alberta’s renewable energy moratorium (August 2023 to February 2024) created additional uncertainty. While the moratorium technically lifted, the provincial government imposed significant new restrictions on renewable development: bans on renewable projects on high-quality agricultural land, 35-kilometre viewscape buffer zones around "pristine view" designations, and an overarching "agriculture first" policy [13]. These conditions effectively maintained the moratorium [22].

Assessment. Alberta shows that market-driven flexibility can support grid reliability and contribute positively to system stability. Climate alignment requires additional instruments: binding carbon-intensity standards and renewable procurement requirements. Without these, Alberta’s competitive advantage in attracting miners functions as an emissions subsidy. Off-grid flare-gas operations offer measurable methane-abatement value, but claims require verification against measured abatement outcomes rather than reliance on promotional narratives.

Manitoba: Moratorium to Conditional Reintegration

Manitoba’s abundant hydroelectric resources attracted extraordinary interest. By late 2022, Manitoba Hydro reported that connecting all interested cryptocurrency-mining operators would have added roughly 4,600 MW of load, far exceeding available system capacity, and the province directed a pause on new connections [23].

The province imposed an 18-month moratorium on new crypto-mining connections in November 2022 [23]. In April 2024, Manitoba directed Manitoba Hydro to extend the pause until April 30, 2026, to allow further analysis [24]. In the bill-status packet captured on May 17, 2026, Bills 20 and 39 had advanced to concurrence and third reading on May 6, 2026, with Royal Assent still blank in the May 13, 2026 bill-status PDF. Bill 20 would authorize a curtailable power program for cryptocurrency operations, and Bill 39 would establish separate customer classes and a levy that can reach 100 percent of monthly energy and demand charges if no lower rate is prescribed [29] [30] [33].

Assessment. Manitoba’s moratorium was proportionate to the scale of proposed demand relative to system capacity. The 2026 legislative response moves the province from a temporary pause toward selective reintegration through curtailment authority and differentiated pricing. The remaining policy issue is calibration: curtailment criteria, levy rates, and customer-class definitions must distinguish grid-supportive flexible load from ordinary consumption of scarce hydro capacity.

III. International Policy Transferability

Texas: Flexible Loads Through Real-Time Pricing

Texas has established itself as a leading mining jurisdiction by leveraging its deregulated ERCOT market. Miners respond to real-time electricity pricing, reducing loads during peak conditions and earning compensation through ancillary services and energy resale. Riot Platforms received $31.7 million in combined power and demand-response credits in a single month (August 2023), comprising approximately $24.2 million in power-curtailment credits under its ERCOT contract and $7.4 million from ERCOT’s demand-response program [25]. The company curtailed power usage by over 95 percent during peak demand periods.

Transferability. Canadian provinces with wholesale electricity markets (Alberta, Ontario) could formally integrate mining loads into existing demand-response or capacity markets. Provinces with regulated utilities (BC, Manitoba) might instead structure interruptible tariffs. The key lesson is mechanism transfer: price-exposed or contract-bound flexibility as a planning instrument.

European Union: Efficiency Standards and Heat Recovery Mandates

Under the Energy Efficiency Directive (EED), the EU mandates detailed reporting of Power Usage Effectiveness (PUE) and encourages waste heat recovery for large data centres [15]. Some EU jurisdictions require new data centres to connect directly to district heating systems or demonstrate feasible heat recovery [16]. The EU also explores sustainability labels for mining facilities meeting environmental benchmarks.

Transferability. Provincial regulators or Natural Resources Canada could set minimum PUE thresholds and mandatory feasibility studies for waste heat reuse above a defined capacity. A "green mining" certification system would provide market differentiation for compliant operators.

China: Restriction and Displacement Logic

China dominated global Bitcoin mining before implementing a complete ban in 2021. The ban succeeded in eliminating domestic mining; it redistributed rather than eliminated global mining activity, with operations migrating to jurisdictions with less regulated grids and producing uncertain net global emissions effects [17].

Transferability. Hard prohibition reduces domestic exposure while redistributing emissions globally. Conditional access gives regulators a more discriminating instrument than prohibition alone: carbon-intensity-based approval thresholds where provinces restrict or disincentivize facilities on high-emission grids unless operators secure verified renewable procurement or carbon offsets achieve net climate benefits.

IV. Metrics and Quantification for Energy Circularity

The metrics framework defined in Appendix B (Table B.1) provides the quantitative basis for comparing two policy scenarios for Bitcoin mining expansion in Canada. Hardware-efficiency benchmarks captured in the May 17 refresh route are lower than the conservative values used in the earlier scenario frame: the Antminer S21 Pro listing reports 15 J/TH, the network-wide average reached approximately 15.2 J/TH as of January 2026 [26], and the Antminer S23 Hyd listing reports 9.5 J/TH [27]. The 25 J/TH value for latest ASICs reflects a generation of hardware that is now mid-tier in the captured materials, and the Scenario B target of 15 J/TH is already the global average rather than an aspirational benchmark. The scenario tables below are corrected accordingly.

Scenario A: Business-as-Usual

Minimal new policy intervention. Provinces with existing restrictions or moratoria (BC, Manitoba) maintain them. New mining activity concentrates in provinces with fewer regulations, primarily Alberta, Saskatchewan, Ontario, and Atlantic Canada. The 1,000 MW figure is an illustrative stress case, extrapolated from a rough 500-700 MW capacity estimate and older 6-10 percent hashrate-share assumptions, then moderated for post-halving margin compression and AI data centre competition. The downstream values are scenario placeholders for sensitivity analysis rather than forecast outputs. Key outcomes:

  • Renewable energy share falls from current levels near 75 percent to approximately 40 percent as Alberta’s fossil-dependent grid absorbs most new capacity.

  • Annual carbon emissions rise to an order-of-magnitude estimate near 3.5 Mt CO2 per year, with Alberta carrying most of that burden under the assumed load distribution.

  • Heat recovery stays limited at under 10 percent nationally. Operations in fossil-dependent regions typically occur in remote areas lacking nearby users for waste heat recovery.

  • Demand-response capability remains modest: approximately 150 MW (15 percent of total load), dependent solely on voluntary market behaviour.

  • Facility-level efficiency averages approximately 1.10 PUE. Average hardware efficiency settles around 17 J/TH as post-halving competition forces mid-tier hardware retirement while failing to drive frontier adoption.

  • Employment stays limited at 1 to 2 direct jobs per 10 MW installed.

  • Grid impacts trend negative in this scenario because continuous load in fossil-heavy grids can elevate local electricity prices.

Scenario B: Circular Economy Policy Integration

Coordinated policy interventions distribute the same illustrative 1,000 MW mining load across provinces under enforceable renewable energy, heat recovery, emissions, and demand-response requirements:

  • British Columbia: permits 200 MW under mandatory heat-utilization agreements tied to district heating or industrial heat users. (This allocation assumes a reversal of BC’s current trajectory toward prohibition, conditioned on audited circular value.)

  • Quebec: authorizes 300 MW contingent on minimum heat-recovery requirements and peak-hour curtailment capability.

  • Manitoba: approves 100 MW linked to surplus wind generation and agricultural heat applications.

  • Alberta: allows 300 MW, split between grid-connected facilities subject to carbon-offset requirements and off-grid operations utilizing verified flare-gas abatement.

  • Ontario and other provinces: combined 100 MW pilot program for grid-balancing services.

Illustrative outcomes requiring sensitivity analysis:

  • Renewable energy share reaches approximately 85 percent as hydro, wind, solar, and nuclear baseload dominate the supply mix.

  • Carbon emissions decrease to an illustrative range of approximately 0.6-0.7 Mt CO2 per year before any verified methane-abatement credit. Off-grid flare-gas operations in Alberta would need project-level verification before being treated as net-emissions reductions.

  • Heat recovery reaches 30 to 40 percent nationally only if co-location, district-heating, agricultural, or industrial heat-use assumptions hold. Approximately 350 MW of continuous heat (roughly 3 million MWh annually) becomes usable energy under that scenario frame, offsetting fossil-fuel heating equivalent to approximately 550,000 tonnes of CO2 per year.

  • Demand-response capability expands to approximately 600 MW (60 percent of total load), providing peak-load reduction and intermittent renewable energy balancing.

  • Facility efficiency improves to approximately 1.05 PUE. Average hardware efficiency reaches approximately 14-15 J/TH (corrected from initial 12 J/TH assumption). Post-halving margin compression limits frontier adoption despite higher efficiency hardware.

  • Employment per MW installed increases two to three times through integration with district heating, agricultural, and industrial heat consumers.

  • Grid impacts could become positive if curtailment, renewable matching, and heat-use assumptions hold.

The comparative outcomes are summarized in Appendix B, Table B.2.

V. Policy Recommendations

Recommendation 1: Mandatory Demand Response Integration

For mining to qualify as a managed grid participant rather than ordinary high-density load, provincial approvals would need to require demand-response participation for facilities above 5 MW. Utilities would establish interruptible tariffs providing reduced off-peak rates in exchange for curtailment during peak demand or emergencies. Facilities would install smart metering enabling utility-verifiable load control. Provincial utility commissions would oversee tariffs to prevent cross-subsidization. Interprovincial standards coordinated through the Canadian Council of Energy Ministers would limit rule-shopping across provincial electricity systems.

Recommendation 2: Mandatory Waste Heat Recovery

Provincial approvals would also need a heat-recovery screen for mining facilities exceeding 1 MW. Operators would submit standardized Heat Reuse Feasibility Studies during the project approval process, detailing potential local heat users: district heating systems, agricultural operations, or industrial processes. Where feasible pathways exist, implementation becomes a condition of interconnection. Facilities failing to implement feasible heat reuse face financial penalties or higher tariffs. Municipal zoning can encourage co-location of mining with district heating infrastructure, agricultural heat users, or industrial heat demand.

Recommendation 3: Renewable Energy Matching and Carbon Intensity Standards

Approvals would need either renewable energy procurement obligations or carbon-intensity ceilings for mining operations. Options include Renewable Portfolio Standards mandating progressive procurement increases, reaching full renewable sourcing by 2030; or maximum carbon-intensity benchmarks requiring miners on high-emission grids to offset emissions exceeding defined thresholds through verified procurement or offsets. Annual third-party audits would document compliance. National harmonization would reduce jurisdiction-shopping.

Recommendation 4: Public Transparency and Reporting

Standardized disclosure tables would cover curtailment performance, energy mix, heat delivery volumes, and emissions factors by site class. Public reporting would document community value claims and support interprovincial performance comparison.

VI. Unintended Consequences and Mitigation

Integrating Bitcoin mining into Canada’s circular economy carries risks that require explicit management:

a. Emissions leakage. Overly restrictive local regulations redirect mining to fossil-dependent jurisdictions, increasing net global emissions. Coordinated interprovincial standards and economic incentives for renewable-powered mining limit this risk.

b. Market distortion. Excessively low electricity tariffs for miners impose costs on other ratepayers. Transparent pricing reflecting true energy and infrastructure costs prevents cross-subsidization. Competitive bidding processes, similar to Quebec’s allocation approach, distribute costs fairly.

c. Competition for grid capacity. Mining load growth now competes directly with AI and data-centre demand for the same provincial grid capacity. Explicit integration of projected mining loads into provincial resource and infrastructure planning, alongside competing high-density demands, prevents uncoordinated allocation.

d. Threshold gaming. Operators may fragment operations or deploy behind-the-meter installations to avoid regulatory thresholds. Lower trigger thresholds, consistent inter-provincial application, and systematic utility monitoring of unexpected load growth address this risk.

e. Electronic waste. ASIC replacement cycles are accelerating post-halving as tighter margins force rapid hardware turnover. Extended Producer Responsibility (EPR) programs, formal inclusion of mining hardware in provincial e-waste recycling frameworks, and resale or repurposing incentives are necessary.

f. Community and social impacts. Noise, siting conflict, and perceived resource competition can undermine local acceptance. Proactive community engagement, benefit-sharing agreements, strict noise enforcement, and appropriate zoning standards are essential.

g. Stranded asset risk. The April 2024 halving and continued difficulty increases accelerate hardware obsolescence. Miners operating on thin margins face stranded capital, potentially abandoning sites with unresolved environmental obligations. Interconnection agreements should require performance bonds or site remediation guarantees.

VII. Conclusion

The provincial divergence in Canadian electricity systems means that no single national policy posture toward Bitcoin mining is coherent. The decisive issue is the conditional architecture: the specific instruments that transform an undifferentiated energy load into a managed, measurable, and accountable grid participant.

Quebec’s framework shows how institutional control over capacity allocation, pricing, and interruptibility can prevent disorderly expansion while preserving circular economy potential. British Columbia’s trajectory from moratorium to effective prohibition illustrates the political cost when planning systems cannot absorb demand at scale. Alberta’s market flexibility produces grid reliability benefits but requires binding environmental constraints to prevent functioning as an emissions subsidy. Manitoba’s extended moratorium is proportionate to system-scale risk but needs a defined post-moratorium framework to avoid becoming permanent exclusion by default.

Bitcoin mining converts electricity to computation with no material reuse cycle. The circular economy framing therefore belongs to the waste-heat recovery and grid-services components of Scenario B, where mining’s thermal and load-balancing by-products are captured for productive use. The mining itself remains extractive; the policy question is whether capturing its by-products justifies tolerating the extraction.

The MintGreen project indicates that high heat recovery is technically achievable under specific conditions (as reported by the company and CoinDesk): immersion cooling, proximity to a district heating network, and a willing municipal utility partner. These conditions are not present at most potential mining sites. The gap between a single demonstration project and the Scenario B target of 30-40 percent national heat recovery is substantial and depends on co-location incentives, municipal partnerships, and capital investment still absent at national scale. Texas shows that demand-response integration can generate tens of millions of dollars in grid-stabilization value per facility. Hardware efficiency has advanced from 25 J/TH to below 10 J/TH in two generations, compressing the energy cost per unit of computation.

Institutional architecture carries the policy burden. Mandatory interruptibility, audited heat recovery, binding carbon-intensity standards, and public transparency are baseline conditions for treating Bitcoin mining as part of Canada’s circular energy economy. Under that architecture, mining may become a flexible, measurable, and accountable participant in provincial grid management. Outside it, mining remains opportunistic demand that follows rule gaps.

The recommendations assume interprovincial coordination, which faces substantial political obstacles. Scenario B likely requires federal-provincial coordination, but that coordination remains politically contentious. Absent coordination, Scenario A (business-as-usual with high-carbon concentration in permissive jurisdictions) is more plausible than the coordinated Scenario B. Whether mining becomes a "flexible load" depends on political circumstances for coordination more than technical feasibility.

Four date-sensitive limitations remain. First, the scenario values are illustrative rather than model-certified. The 1,000 MW stress case, emissions estimates, heat-recovery offsets, demand-response capacity, and employment multipliers require a sensitivity appendix before formal circulation. Second, legal status is live: provincial statutes, utility tariffs, customer-class rules, and moratoria require same-day refresh before policy circulation. Third, heat-recovery evidence rests heavily on company-facing or demonstration evidence; national scaling claims require independent performance verification, site suitability analysis, and co-location assumptions. Fourth, Bitcoin energy estimates move with hardware efficiency, hashrate, price, mining geography, and grid mix. Any circulated version should archive CBECI, hardware-efficiency, provincial-grid, and legal sources on the version date.

References

[1] Cambridge Centre for Alternative Finance, "Bitcoin mining: an (un)surprising resurgence?," Cambridge Judge Business School, May 17, 2022. Available online.

[2] S. Chamanara, S. A. Ghaffarizadeh, and K. Madani, "The environmental footprint of Bitcoin mining across the globe: call for urgent action," Earth’s Future, vol. 11, no. 10, Art. no. e2023EF003871, Oct. 2023. DOI: 10.1029/2023EF003871.

[3] B. Brown, "Crypto-friendly Quebec discounts electricity, luring Bitcoin miners into Canada," CCN, Mar. 4, 2021. Available online.

[4] Hydro-Quebec, "Hydro-Quebec launches a request for proposals regarding the allocation of a 300 MW block of capacity," Press Release, Jun. 5, 2019. Available online.

[5] K. Dangerfield, "Bitcoin’s fossil fuel use criticized. But some Canadian companies hope to turn it green," Global News, May 13, 2021. Available online.

[6] Hydro-Quebec, "A new rate for data centres and a rate adjustment for blockchains to reflect the value of renewable electricity," News Release, Feb. 19, 2026. Available online.

[7] Gouvernement du Quebec, "Cryptomonnaies : la Regie de l’energie rend une decision," Jan. 28, 2021. Available online.

[8] Government of British Columbia, "New legislation ensures B.C. benefits from clean, affordable electricity," News Release, Apr. 11, 2024. Available online.

[9] K. J. Howard, D. Nikolejsin, V. Lucas, R. Carlson, and K. E. Griffin, "Amping up the rules: BC to regulate crypto-mining electricity use," McCarthy Tetrault LLP, May 17, 2024. Available online.

[10] MintGreen, "North Vancouver to be World’s First City Heated by Bitcoin," Oct. 14, 2021. Available online.

[11] S. Kennedy, "Canadian oil producer mines bitcoin, snuffs out gas flare," Energy Flux, May 9, 2021. Available online.

[12] Canada Energy Regulator, "Provincial and territorial energy profiles: Alberta," Government of Canada, 2023. Available online.

[13] J. Wang and W. Noel, "Investment impact of Alberta’s renewable energy moratorium," Pembina Institute, Aug. 24, 2023. Available online.

[14] A. Ashraf, "Riot Blockchain mined 28% less Bitcoin in July as heat wave cut power supply," CoinDesk, Aug. 3, 2022. Available online.

[15] European Commission, "Commission adopts EU-wide scheme for rating sustainability of data centres," Mar. 15, 2024. Available online.

[16] D. Barcaba and E. Kaufman, "Impact of the Energy Efficiency Directive and the Energy Efficiency Act on companies, especially data centre operators," Bird and Bird LLP, Dec. 16, 2024. Available online.

[17] N. Smith, "Countries say no to energy guzzling Bitcoin mines," Greenpeace USA, May 14, 2024. Available online.

[18] Cambridge Centre for Alternative Finance, "Cambridge Bitcoin Electricity Consumption Index methodology," Cambridge Digital Assets Programme, accessed May 2026. Available online.

[19] MiCA x Nodiens, "The carbon footprint path to 2030," 2025. Available online.

[20] Hydro-Quebec, "Rate CB: Blockchains," customer rate page, accessed 2026. Available online.

[21] CoinDesk, "How a Startup Is Supplying a Whole City With Heat From Bitcoin Mining," Oct. 14, 2021. Available online.

[22] Environmental Law Centre (Alberta), "Renewables moratorium shifted not lifted," 2024. Available online.

[23] Manitoba Hydro, "Province directs Manitoba Hydro to pause new cryptocurrency connections," Nov. 2022. Available online.

[24] Manitoba Hydro, "Province directs Manitoba Hydro to continue pause on new cryptocurrency connections," Apr. 2024. Available online.

[25] Houston Chronicle, "One bitcoin company received millions to reduce electricity use," Sept. 2023. Available online.

[26] Bitcoin Power Consumption, "Bitcoin average joules per terahash," 2026. Available online.

[27] ASIC Miner Value, "SHA-256 miners efficiency," 2026. Available online.

[28] Legislative Assembly of Manitoba, "3rd Session - 43rd Legislature, Social & Economic Development 2," Apr. 22, 2026. Available online.

[29] Legislative Assembly of Manitoba, "Bill 20: The Manitoba Hydro Amendment Act," 3rd Session, 43rd Legislature, 2026. Available online.

[30] Legislative Assembly of Manitoba, "Bill 39: The Manitoba Hydro Amendment and Tax Administration and Miscellaneous Taxes Amendment Act," 3rd Session, 43rd Legislature, 2026. Available online.

[31] Government of British Columbia, "Permanent ban on new BC Hydro connections for cryptocurrency mining," News Release, Oct. 20, 2025. Available online.

[32] Government of British Columbia, "Cryptocurrency Power Regulation, B.C. Reg. 163/2024," current to 2026. Available online.

[33] Legislative Assembly of Manitoba, "Status of Bills, Third Session, Forty-Third Legislature, 2025-2026," last updated May 13, 2026. Available online.

Appendix A: Terms and Definitions

ASIC (Application-Specific Integrated Circuit): Specialized hardware designed specifically for cryptocurrency mining, offering high computational efficiency relative to general-purpose hardware. Current frontier: Antminer S23 Hyd at 9.5 J/TH.

Carbon intensity: CO2 emissions produced per unit of electricity consumed, typically expressed as kg CO2 per MWh. Alberta’s grid intensity has declined substantially with coal-to-gas transition (completed June 2024) but remains far above hydro-dominant provinces.

Carbon offset: Verified emissions reductions achieved through renewable energy investment, methane capture, reforestation, or other removal and abatement pathways.

Circular economy: An economic design model focused on resource reuse, waste minimization, and lifecycle efficiency. In the mining context, the primary instruments are waste heat recovery and demand-response grid integration.

Community benefit funds: Financial mechanisms directing a portion of mining revenue into local infrastructure, economic development, or environmental enhancement.

Demand response (DR): Load adjustment in response to grid stress, pricing signals, or emergency events. Distinct from voluntary curtailment: contracted DR is dispatchable and verifiable; voluntary curtailment is not.

Electronic waste (e-waste): End-of-life electrical and electronic equipment, including retired ASIC mining hardware. ASIC replacement cycles are accelerating post-halving.

Extended Producer Responsibility (EPR): Policy model requiring producers to manage end-of-life environmental impacts through recycling, recovery, or responsible disposal.

Hashrate: Total computational mining power, typically expressed in TH/s, PH/s, or EH/s. Higher hashrate indicates greater computational and energy expenditure.

Hashing: The computational process of transforming input data into a fixed-length output, used in mining to validate transactions and maintain blockchain consensus.

Interruptible power contracts: Utility agreements permitting curtailment during peak conditions in exchange for preferential pricing. Distinct from voluntary market-driven curtailment.

Methane flare-gas utilization: Use of otherwise flared or vented methane from oil and gas production for electricity generation, including mobile mining contexts. Claims require verified measurement of actual methane abatement.

Moratorium: A temporary administrative suspension on new project approvals or electricity interconnections.

Power Usage Effectiveness (PUE): Total facility power divided by IT equipment power. Lower values indicate better infrastructure efficiency. Industry benchmark for optimized facilities: 1.05 or below.

Interprovincial rule-shopping: Exploiting rule differences across jurisdictions to reduce compliance burden. Particularly relevant in Canadian federation where provinces set divergent electricity and environmental standards.

Renewable energy share: Percentage of total electricity consumption sourced from renewable generation (hydro, wind, solar, biomass).

Terahash (TH): One trillion hashing operations per second.

Waste heat recovery: Capture and beneficial reuse of thermal output from mining operations, typically for district heating, agricultural, or industrial applications.

Appendix B: Metrics and Scenario Tables

Table B.1: Key Metrics for Bitcoin Mining Energy Analysis

Metric Definition / Formula Significance and Targets

Joules per Terahash (J/TH)

Device power (W) divided by hashrate (TH/s)

Hardware efficiency. Current frontier: 9.5 J/TH (S23 Hyd). Network average: ~15.2 J/TH (Jan 2026). Mid-tier: 17 to 25 J/TH. Obsolete: 30+ J/TH.

Power Usage Effectiveness (PUE)

Total facility power divided by IT equipment power

Infrastructure efficiency. Typical: ~1.10. Target: 1.05 or below. Heat-reuse-integrated facilities can approach 1.02.

Renewable Energy Share (%)

Renewable MWh divided by total MWh, multiplied by 100

Sourcing sustainability. BC: ~98%. QC: ~95%. AB: ~19% (2024). Global mining average: ~41% (2024) [19].

Carbon Intensity

kg CO2 per MWh, derived from provincial grid emission factor

Climate impact. BC hydro: near zero. QC hydro: near zero. AB grid: declining but substantially higher. Target: province-specific thresholds with offset obligations.

Heat Recovery Rate (%)

Recovered heat divided by total waste heat, multiplied by 100

Circularity performance. Achievable with immersion/district heating: up to 96% (MintGreen). Typical without recovery: 0%. Target for large facilities: 30% or above.

Demand Response Capacity

MW curtailable plus annual event hours utilized

Grid support. Riot Platforms demonstrated 95%+ curtailment in peak events, earning $31.7M in a single month (Aug 2023).

CO2 Offset via Heat/DR

Tonnes CO2 avoided annually through heat reuse or DR curtailment

Net environmental benefit. 1 MW with 80% heat reuse offsets approximately 1,260 tCO2/year.

Jobs per 10 MW

Direct employment per 10 MW of installed mining load

Socio-economic value. Mining alone: roughly 1 to 2 direct jobs per 10 MW in this scenario frame. Heat-utilization integration may add jobs through recipient industries, but the multiplier requires local evidence.

Table B.2: Illustrative Scenario Outcomes with Sensitivity Range

Metric Scenario A: Business-as-Usual Scenario B: Circular Policy Integration

Total mining load

1,000 MW concentrated regionally

1,000 MW distributed nationally

Renewable energy share

~40% (fossil-heavy grid absorption)

~85% (renewable and low-carbon supply)

Annual CO2 emissions

Order-of-magnitude estimate near 3.5 Mt CO2

Illustrative range of ~0.6-0.7 Mt CO2

Waste heat utilization

Under 10%

30 to 40% sensitivity case

CO2 offset from heat reuse

~0.1 Mt CO2 annually

Up to ~0.55 Mt CO2 annually under co-location assumptions

Net CO2 impact

+3.4 Mt net emissions

+0.1 to +0.2 Mt net (after correcting hardware efficiency assumption)

Average PUE

1.10

1.05

Hardware efficiency (J/TH)

~17 J/TH (mid-tier fleet post-halving)

~15 J/TH (realistic under capital constraints)

Demand-response flexibility

~150 MW (voluntary only)

~600 MW (contracted and dispatchable)

Grid impact

Neutral to negative

Potential stabilization under enforceable curtailment

Economic co-benefits

Low multiplier (1 to 2 jobs/10 MW)

Higher local value through heat integration

Policy goals alignment

High-emissions pathway with minimal circularity

Conditional alignment under audited heat recovery and low-carbon supply