For decades before market restructuring, the region’s utilities operated as vertically integrated, rate-payer-funded, regulated monopolies that generated, transmitted, and distributed electricity. Dissatisfied with investments that increased consumer rates while limiting funds for needed infrastructure, the federal government and the New England states introduced a new industry framework in the late 1990s: competitive, technology-neutral wholesale markets where privately developed resources would compete with each other to provide the least-cost, reliable wholesale electricity supply. The goals of competitive wholesale electricity markets were to lower costs, encourage innovation, and shield consumers from unwise investments. (Learn about ISO New England’s responsibility for administering the region’s wholesale electricity markets.)
During this time, the New England states also began introducing clean energy incentives and emission-reduction goals, focusing first on reducing greenhouse gas (GHG) emissions from the electric power industry. Emissions regulations work well with the wholesale markets by making higher-polluting power plants more expensive to operate and providing a reliable means for cleaner resources to come on line in their place.
Over the past 20 years, the market and policy approach has driven change in the direction the states have been seeking, spurring private investment in some of the most efficient, lowest-emitting power resources in the country, shifting investment costs and risks away from consumers, lowering wholesale prices, reducing carbon emissions, and enabling the transition to a system that emits even less carbon.
When the wholesale markets opened to competition two decades ago, private companies invested billions of dollars in the development of natural-gas-fired power plants because they used advanced technology that made them run efficiently; were relatively inexpensive to build, site, and interconnect; and their lower carbon emissions compared to coal and oil plants helped the region meet state environmental policies. As lower-cost, highly efficient natural gas plants displaced older oil and coal plants in New England, wholesale electricity prices declined.
Natural gas is now the predominant fuel in New England, used to generate 55% of the electricity produced by the region’s power plants in 2023. As a result, the price of this single fuel sets the energy market price most of the time—so the prices of natural gas and wholesale electricity are closely linked. The high efficiency of natural-gas-fired generators and the generally low cost of nearby domestic shale gas (which emerged as a resource in 2008) are largely responsible for the significant decrease in the average annual price of New England’s wholesale electricity over the past 16 years, after prices plummeted almost 50% following the shale gas boom. Lower wholesale prices translate into lower power-supply charges for consumers.
The COVID-19 pandemic and the continuation of regional industry trends led to historically low consumer demand for grid electricity in New England in 2020, setting the stage for the lowest average wholesale market prices since the inception of the region’s competitive markets in 2003. Wholesale power prices have increased since then, driven by rising natural gas prices.
Higher real-time power prices in 2013, 2014, 2018, and in 2021–2022 were largely due to winter spikes in natural gas prices. When natural gas is constrained and at a premium—or when global market forces lead to high natural gas prices—oil generation may become more economic. High prices are an expected and efficient market outcome when system conditions are tight—signaling a system need. Winter prices will continue to exhibit volatility reflective of the fuel and weather constraints that limit the ability of power resources to produce electricity during extended cold conditions.
Power resources compete in the Forward Capacity Market to take on a commitment to be available to meet projected demand for electricity three years out. Whereas the energy market value varies with fuel prices, the capacity market value varies with changes in amounts of electricity-producing and demand-reducing resources.
Strong competition has generally kept capacity market auction prices low for most years. The capacity market works in tandem with the energy and ancillary service markets to provide revenue that attracts and sustains power resources needed today and into the future. Over the years, the FCM has enabled participation of energy efficiency and demand response programs, as well as new resources including renewable energy facilities and natural gas plants. And it has provided an orderly process for the retirement of nearly 8,000 MW from older fossil fuel units and nuclear plants.
Despite significantly reduced emissions from the power system, action toward meeting economywide GHG goals set by the states is just getting underway. There is a growing desire to accelerate actions needed to meet the climate goals. With deadlines looming, the states are eager for the quicker transformation of the power grid to renewables and for electrification of the broader economy.
Because large-scale renewable resources typically have higher up-front capital costs and different financing opportunities than more conventional resources, they have had difficulty competing in the wholesale markets. Therefore, the New England states are promoting, at varying levels and speed, the development of specific clean-energy resources to meet their public policy goals.
Several states have established public policies that direct electric power companies to enter into rate-payer-funded, long-term contracts for large-scale carbon-free energy that would cover most, if not all, of the resource’s costs. Long-term contracts carry risk given the rapid development and falling costs of new technologies—and this risk of stranded costs is placed back on consumers. As policymakers seek to convert the transportation and heating sectors to carbon-free electricity to fully meet climate goals, this public policy trend is expected to continue.
Pricing carbon within the competitive market structure is the simplest, easiest, and most efficient way to rapidly reduce GHG emissions in the electricity sector. Moreover, placing a realistic price on carbon would enable consumers to pay accurate, competitive prices without the risk of paying for stranded costs. However, New England state policymakers and other stakeholders responsible for putting this approach into motion have not pursued a carbon-pricing option that effectively reflects decarbonization goals, neither economywide nor in the electricity sector.
Annual auctions in the Forward Capacity Market (FCM) ensure the system has sufficient resources to meet future electricity demand. Obligations to provide capacity are determined through these auctions three years before the commitment period. Resources that clear receive monthly payments during the capacity year in exchange for their commitment to be available to meet the projected demand for electricity. That delivery period is called the capacity commitment period (CCP)—a one-year timeframe from June 1 through May 31 of the following year. As the year of need gets closer, monthly capacity auctions also take place.
Auction Commitment Period |
Total Capacity Acquired (MW) | New Demand Resources (MW)1 |
New Generation (MW)2 |
Clearing Price ($/kW-month)3 |
---|---|---|---|---|
FCA 18 in 2024 for CCP 2027/2028 | 31,556 | 105 | 998 | $3.580 |
FCA 17 in 2023 for CCP 2026/2027 | 31,370 | 130 | 619 | $2.590 |
FCA 16 in 2022 for CCP 2025/2026 | 32,810 | 230 | 311 | ROP: $2.591 NNE: $2.531 & SENE: $2.639 |
FCA 15 in 2021 for CCP 2024/2025 | 34,621 | 170 | 950 | ROP: $2.611 NNE: $2.477 & SENE: $3.980 |
FCA 14 in 2020 for CCP 2023/2024 | 33,956 | 323 | 335 | $2.001 |
FCA 13 in 2019 for CCP 2022/2023 | 34,839 | 654 | 8374 | $3.800 |
FCA 12 in 2018 for CCP 2021/2022 | 34,828 | 514 | 174 | $4.631 |
FCA 11 in 2017 for CCP 2020/2021 | 35,835 | 640 | 264 | $5.297 |
FCA 10 in 2016 for CCP 2019/2020 | 35,567 | 371 | 1,459 | $7.030 |
FCA 9 in 2015 for CCP 2018/2019 | 34,695 | 367 | 1,060 | System-wide: $9.551 SEMA/RI: $17.728/new & $11.080/existing |
FCA 8 in 2014 for CCP 2017/2018 | 33,712 | 394 | 30 | $15.000/new & $7.025/existing |
FCA 7 in 2013 for CCP 2016/2017 | 36,220 | 245 | 800 | $3.150 (floor price) NEMA/Boston: $14.999 |
FCA 6 in 2012 for CCP 2015/2016 | 36,309 | 313 | 79 | $3.434 (floor price) |
FCA 5 in 2011 for CCP 2014/2015 | 36,918 | 263 | 42 | $3.209 (floor price) |
FCA 4 in 2010 for CCP 2013/2014 | 37,501 | 515 | 144 | $2.951 (floor price) |
FCA 3 in 2009 for CCP 2012/2013 | 36,996 | 309 | 1,670 | $2.951 (floor price) |
FCA 2 in 2008 for CCP 2011/2012 | 37,283 | 448 | 1,157 | $3.600 (floor price) |
FCA 1 in 2008 for CCP 2010/2011 | 34,077 | 1,188 | 626 | $4.500 (floor price) |
1 Not counted as new is the demand-resource type once known as real-time emergency generation (RTEG). RTEG resources, which participated in FCAs 1 through 7, were treated as existing capacity and capped at 600 MW.
2 Some new capacity reflects increased capacity at existing resources.
3 Additional auction information, including pricing for import interfaces, is included in the Forward Capacity Auction Results file.
4 This total includes new generation acquired in both the primary auction (783 MW) and substitution auction (54 MW).