 
 
 
 INSIGHTi  
Clean Air Act: Electricity Sector and 
Greenhouse Gas Standards 
March 12, 2021 
Congress may continue to exami
ne Clean Air Act (CAA) authorities and climate change issues as it 
deliberates on legislation  and conducts oversight of the U.S. Environmental Protection Agency (EPA).  
The Biden Administration has committed to reducing greenhouse gas (GHG) emissions using various 
policy tools to achieve a 
“carbon pollution-free electricity sector” by 2035. Multiple factors, including 
economics, technology, and energy and climate policies, could play a role in future GHG emission levels. 
Many say both legislative and executive actions would be necessary to decarbonize the electricity sector 
by the Administration’s target date. 
Electricity Sector GHG Emissions 
Since 1990, GHG emissions fr
om fossil fuel combustion ha
ve accounted for 74%-78% of total U.S. GHG 
emissions. The electricity sector historical y accounted for the largest percentage of U.S. GHG emissions 
from fossil fuel combustion, but has been surpassed by t
he transportation sector since 2016.  
Carbon dioxide (CO2) emissions from fossil fuel combustion in the electricity sector declined by 25% 
between 2008 and 2018. Multiple factors
, including overal  economic conditions and electricity market 
developments, played a role in this decline. O
ne key factor involves the U.S. electricity generation 
portfolio. The contributions of different fuels and energy sources within the portfolio changed in recent 
years, which in turn altered emission levels.  
Clean Air Act 
Since the 1970s, EPA has promulgated rules under CAA  Section 111 and other CAA authorities to limit 
non-GHG emissions, such a
s sulfur dioxide, nitrogen oxides, a
nd mercury, from power plants. In the past 
decade, EPA has used CAA  Section 111 authority to promulgate regulations addressing GHG emissions 
from these sources.  
CAA  Section 111 requires EPA to establish national y  uniform, technology-based performance standards 
for categories of industrial facilities, also cal ed stationary sources, that cause or contribute significantly 
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to air pollution that may endanger public health or welfare
. Section 111(b) directs EPA to establish 
maximum emission levels 
(New Source Performance Standards, or NSPS) for new and modified major 
stationary sources. To set the NSPS, EPA determines t
he best system of emission reduction (BSER) that 
has been 
“adequately demonstrated,” taking into account costs and any non-air-quality health and 
environmental impact and energy requirements.  
Once EPA promulgates NSPS under Section 111(b), Section 111(d) requires EPA to promulgate 
regulations for existing sources. The Section 111(d) rules set procedures for states to submit plans 
establishing performance standards for existing sources that would be subject to NSPS if they were new, 
barring an exclusion under Section 111(d). 
New Power Plants 
In 2015, EPA promulgate
d GHG performance standards for new and modified power plants under CAA 
Section 111(b) concurrent with the 111(d) standards for existing plants (discussed below). The 2015 GHG 
NSPS for new and modified power plants relied partly on carbon capture and sequestration (CCS). In 
2018, EPA proposed, among other things, to replace the BSER determination for new coal units (i.e., 
partial CCS) with a determination that BSER  for these units would be the most efficient demonstrated 
steam cycle in combination with best operating practices. To date, EPA has not finalized the proposed 
revisions to BSER  or the GHG NSPS for new and modified units. The 2015 GHG NSPS for new and 
modified power plants remains in effect. 
Existing Power Plants 
EPA has promulgated two rules under CAA Section 111(d) authority to limit GHGs from existing power 
plants—the 2015 Clean Power Plan (CPP) and the 2019 Affordable Clean Energy (ACE) rule. As 
discussed below, neither rule is in effect.  
CPP 
T
he 2015 CPP set national performance standards for CO2 emissions from existing fossil-fuel-fired power 
plants. One national performance standard would have applied to existing electric steam generating units 
(which are mostly coal), and the other would have applied to existing stationary combustion turbines 
(e.g., natural gas combined cycle units). EPA base
d these standards on the BSER, which the agency 
determined based on a collection of measures: (1) improving t
he heat rate at coal-fired units, (2) shifting 
generation from coal-fired units to lower-emitting natural gas units, and (3) shifting generation from fossil 
fuel units to renewable energy generation. The CPP also se
t individual  state targets. States were to 
determine how to reach these goals. 
The CPP was the subject of ongoing litigation and was never implemented. EP
A repealed the CPP in 
2019. EPA based the repeal on a change in its legal  interpretation of its authority under CAA  Section 111 
from its interpretation in the CPP. EPA concluded that the 2015 CP
P exceeded CAA statutory authority in 
setting the BSER as a combination of 
on- and off-site emission reduction measures that applied to the 
entire existing source category. 
ACE 
EPA finalized  new emissions guidelines for existing coal-fired power plants in the
 2019 ACE rule. The 
ACE rule applied
 a narrower interpretation than the CPP of the BSER, defining it as on-site 
“heat rate 
improvement” measures, also known as efficiency improvements, for existing coal-fired units. EPA 
identified six candidate technologies along with operating and maintenance practices that states were to
  
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 evaluate in establishing a standard of performance for each source in their state plans under CAA Section 
111(d). 
In January 2021, a federal appel ate  cour
t vacated and remanded the ACE rule, directing EPA to 
reconsider its interpretation of its CAA  Section 111(d) authority to regulate GHGs from existing power 
plants. The court also vacated the CPP repeal but stayed its mandate until the EPA responds to the court’s 
remand in a new rulemaking action. 
Issues for Congress 
The CPP and the ACE rule
 presented different legal interpretations of EPA’s CAA  authority. These 
interpretations could raise broader questions about EPA’s approach to regulating GHG emissions under 
the act. 
A related issue is
 what role existing CAA  authority would play in meeting various GHG targets
. It is 
uncertain whether existing CAA authority could achieve the more ambitious targets supported by some 
Members and stakeholders. Congress may consider current and future GHG emissions targets and 
whether and how the CAA authorities could be used to reduce emissions in the electricity sector or 
support complementary policies to meet emissions goals. 
 
 
Author Information 
 Kate C. Shouse 
   
Analyst in Environmental Policy  
 
 
 
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