Analyses / Impact Analysis / 119 · HR 1346 Impact Analysis

119-HR-1346 Investigative Journalist Impact Analysis

119 · HR 1346 Nationwide Consumer and Fuel Retailer Choice Act of 2025

eco Environmental Protection
Nationwide Consumer and Fuel Retailer Choice Act of 2025This bill amends the Clean Air Act to address the limitations on Reid Vapor Pressure (a measure of gasoline's volatility) that are placed on...
Bottom-line assessment
Analytical stance (not advocacy).
E15 average discount vs E10 (2022–Apr 2023 sample)
0.14$/gal
Stations offering E15 (May 8, 2026)
5000stations
Fuel-economy delta: E15 vs E10 (approx.)
-1.7%
Published
14 May 2026
Updated
14 May 2026
Tags
Impact analysis · Clean Air Act · Biofuels
Unvetted
01 · Section

What H.R. 1346 would do

Two operative moves: (1) extend the Clean Air Act’s 1‑psi RVP allowance to blends containing 10–15% ethanol (enabling year‑round E15 nationally) and (2) direct EPA to return or credit specified previously retired RINs (2016–2018) to qualifying small refineries via EMTS. The House passed the bill on May 13, 2026 (218–203). (rules.house.gov)

  • Textual change: replaces “10 percent” with “10 to 15 percent” in CAA §211(h)(4), effectively applying the 1‑psi allowance to E15. (rules.house.gov)
  • Overrides state opt‑outs: for states that previously petitioned to remove the 1‑psi waiver (Midwest eight), the bill would instead apply paragraph (4) to 10–15% blends during high‑ozone season. (rules.house.gov)
  • Small‑refinery provision: returns eligible 2016–2018 RINs to small refineries or posts them to their EMTS accounts for future compliance. (rules.house.gov)
02 · Section

Economic effects

Price effects hinge on station availability, ethanol–gasoline price spreads, and energy‑content tradeoffs; compliance‑credit provisions could shift RIN markets. (eia.gov)

  • Pump prices: EIA notes E15 often prices below E10 when ethanol is cheaper than gasoline blendstock; industry price pairs from 2022–2023 show an average ~$0.14/gal E15 discount vs E10, with wide dispersion. Savings are not guaranteed and vary by market. (eia.gov)
  • Fuel economy: Because ethanol has lower volumetric energy than gasoline, E15 typically yields slightly lower MPG than E10; EIA estimates ~3% MPG loss for E10 vs E0, implying on the order of ~1–2% additional loss going from E10 to E15. Net consumer outlays depend on local price discounts vs this MPG penalty. (eia.gov)
  • Availability and infrastructure: Trade‑group tallies suggest ~4,600 E15 stations at end‑2025 and ~5,000 by May 2026; USDA’s HBIIP grants continue to finance dispenser/tank retrofits, accelerating retail adoption but requiring upfront spend by marketers. (ethanolrfa.org)
  • Refiner compliance costs: Returning specified 2016–2018 RINs to small refineries reverses part of EPA’s 2022 blanket SRE denials (69 petitions), potentially easing near‑term RFS compliance costs for those firms and nudging RIN supply/price. Transactions flow through EMTS. Market impacts depend on volumes and timing. (epa.gov)
  • Distribution/logistics: A nationwide E15 waiver simplifies having a single summer gasoline pool for many markets, but re‑introducing the 1‑psi allowance in states that planned lower‑volatility BOBs can force supply reconfiguration and short‑run costs during transition. EPA’s Midwest RVP rulemaking record and industry filings underscore these frictions. (nepis.epa.gov)
E15 average discount vs E10 (2022–Apr 2023 sample)
0.14$/gal
Stations offering E15 (May 8, 2026)
5000stations
Fuel-economy delta: E15 vs E10 (approx.)
-1.7%
03 · Section

Social effects

Benefits and burdens are uneven—retailers and motorists in regions with robust E15 supply may gain optionality, while agricultural intensification and misfueling risks fall on specific communities and users. (afdc.energy.gov)

  • Rural income and farm revenue: Decades of literature link ethanol expansion with higher farm receipts; more E15 sales plausibly sustain corn demand. However, empirical estimates vary by region and period. (pnnl.gov)
  • Food–feed market signals: A 2022 empirical study attributed about a 30% corn price increase to the RFS in 2008–2016, with spillovers to other crops—effects that can benefit grain producers but raise input costs for livestock and food sectors. (pubmed.ncbi.nlm.nih.gov)
  • Public health exposure: Small engines (lawn equipment, boats) and pre‑2001 vehicles are not approved for E15; Congress’s misfueling‑mitigation and EPA labeling regime seek to reduce inadvertent use, but residual risk falls on households and small businesses operating such equipment. (epa.gov)
  • Groundwater nitrate risk: EPA modeling coupling air–land–water systems indicates increased corn production scenarios can elevate nitrate in groundwater above 5 mg/L in some areas, incrementally raising certain health risks—placing potential burdens on rural well users if corn acreage intensifies. (epa.gov)
04 · Section

Environmental effects

Outcomes diverge by pollutant class: localized ozone‑season volatility management vs. disputed life‑cycle GHG totals and chronic nutrient pressures tied to corn cultivation.

  • Tailpipe/evaporative emissions: EPA has stated its research found no significant change in evaporative emissions when extending the 1‑psi waiver to E15—suggesting limited local air impact where E10 already receives the waiver. (epa.gov)
  • State‑level volatility: EPA finalized removal of the 1‑psi waiver for E10 in eight Midwest states starting with summer 2025 to enable a 9.0‑psi summertime pool; technical support projected reductions in VOC/NOx/CO under that lower‑volatility regime. H.R. 1346 would instead re‑apply the paragraph (4) allowance to 10–15% blends in those states during ozone season—by inference, eroding some modeled reductions. (epa.gov)
  • Life‑cycle GHGs: DOE/Argonne synthesizes recent data to estimate U.S. corn ethanol at roughly 44–52% lower GHG intensity than neat gasoline, while a peer‑reviewed 2022 PNAS assessment (empirical, with domestic land‑use change) concludes corn ethanol is no less than gasoline and likely ≥24% higher—an unresolved methodological divide with material policy implications. (energy.gov)
  • Water quality and habitat: The 2022 PNAS study also associates RFS‑era corn expansion with 3–8% more fertilizer use and 3–5% higher water‑quality degradants; broader USGS work links Corn Belt nutrients to Gulf hypoxia—risks that scale with sustained intensification absent mitigation. (pubmed.ncbi.nlm.nih.gov)
Corn ethanol LCA vs gasoline (DOE/Argonne)
-48%
Corn ethanol LCA vs gasoline (PNAS 2022)
24%
Midwest states with E10 waiver removed (from 2025)
8states
05 · Section

Temporal analysis

Short‑run vs. long‑run trajectories differ across price, supply chains, and environmental externalities.

  • 0–12 months after enactment: Retailers in waiver‑constrained markets can legally sell E15 in summer without emergency waivers; pump prices may show localized discounts where supply exists; small refineries receiving returned RINs get immediate compliance relief via EMTS postings. (epa.gov)
  • 1–5 years: Station build‑out continues (HBIIP grants, retailer investments); ethanol throughput rises if consumer adoption scales, supporting farm income. Countervailing risks include persistence of the MPG penalty and potential ozone‑season volatility reversals in Midwest states if the federal change overrides their 9.0‑psi strategy. (rd.usda.gov)
  • >5 years: Net climate signal remains path‑dependent—on agronomic practice changes, carbon‑intensity improvements at plants, and how land‑use dynamics resolve in the literature; nutrient‑management outcomes in the Corn Belt dominate long‑run aquatic impacts. (energy.gov)
06 · Section

Unintended consequences and secondary effects

Credible risks to watch, based on records and prior rulings.

  • Legal risk/precedent: The D.C. Circuit vacated EPA’s 2019 attempt to extend the 1‑psi waiver to E15; statutory fixes like H.R. 1346 avoid that specific rulemaking vulnerability but could still invite litigation over preemption of state petitions or implementation details. (afpm.org)
  • RIN‑market dynamics: Returning historical RINs may loosen near‑term compliance but introduces retroactive supply into a thin market; EMTS captures transactions but does not reveal full price formation, complicating impact prediction. (epa.gov)
  • Misfueling/consumer confusion: Despite labels and MMP requirements, residual misfueling (small engines, marine) can impose costs on households and small businesses. (epa.gov)
  • Supply‑chain transition costs: Midwest supply was pivoting to lower‑volatility BOBs after EPA’s state‑petition rule; reversing course may add near‑term logistics costs or tightness during the shift. Industry comments flag these frictions. (nepis.epa.gov)
07 · Section

Assessment

Analytical stance (not advocacy).

08 · Section

Sourcing (selected)

Primary law/policy documents, federal data, and peer‑reviewed studies underpin the claims above.

  • Bill text/status: Congress.gov; House Clerk roll; House Rules print. (congress.gov)
  • EPA guidance and actions on E15/RVP/waivers: E15 partial waivers and labeling; RVP program pages; emergency‑waiver statement. (epa.gov)
  • Market/price context: EIA Today in Energy on E15 economics; industry price‑pair dataset. (eia.gov)
  • Infrastructure and availability: USDA HBIIP; trade‑group station counts/sales trend. (rd.usda.gov)
  • GHG and land/water studies: DOE/Argonne synthesis; PNAS 2022 empirical study; USGS nutrient modeling context. (energy.gov)
  • RIN/SRE background: EPA 2022 SRE denials; EMTS program page. (epa.gov)

Discussion