EPA's Response to IPM v6 Peer Review Report
April 2022

Summary of Contents
Section 1: Introduction

Describes the peer review process (goals, charge, panelists), commendations, and the structure
of the rest of the response document in addressing recommendations.

Section 2: Addressing Main Recommendations

2.1	Updates to model to improve the model's ability to represent the ongoing evolution of
the industry: demand/supply, new technologies, transmission, evolving state and
regional policies, and ISO/RTO market rules

2.2	Types of uncertainty that the model handles

2.3	Coal plant turndowns, operating reserves, continued penetration of renewables,
dispatch

2.4	Incorporating upstream emissions

2.5	Investment decision-making of utility and merchant power plants and capacity markets

2.6	Gas markets and natural gas pricing

2.7	Alternative load duration curves changes in load shapes from new forms of demand
(such as electric vehicles); regional and temporal resolution

2.8	Improving representation of behind-the-meter generation

2.9	Increasing transparency of retail pricing model

2.10	Representation of various policy mechanisms and publishing alternative/side cases

2.11	Documentation improvements

Appendix: Table for Detailed Accounting of Peer Review Recommendations and Narrated
Responses

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Response to the Peer Review Report
EPA Reference Case Version 6 Using IPM

U.S. EPA, Clean Air Markets Division

SECTION 1
INTRODUCTION

Background on Peer Review Process

In May 2018, the U.S. Environmental Protection Agency (EPA) released a new version of EPA's
power sector modeling platform (designated Integrated Planning Model (IPM) version 6)1. This
new EPA modeling platform incorporated important structural improvements and data updates
with respect to EPA's previous version (version 5). EPA published several updates to EPA
modeling platform version 6 Reference Case between May 2018 and September 2021.

IPM is a multiregional, dynamic, deterministic model of the U.S. power sector that provides
projections of least-cost capacity expansion, electricity dispatch and emissions. The EPA uses
the platform to project and evaluate the cost and emissions impacts of various policies to limit
emissions of sulfur dioxide, nitrogen oxides, particulate matter, mercury, hydrogen chloride,
and carbon dioxide.

In September 2019, EPA commissioned a peer review of EPA's v6 Reference Case using the
Integrated Planning Model (IPM). Industrial Economics Inc., an independent contractor,
facilitated the peer review of the EPA Version 6 Reference Case in compliance with EPA's Peer
Review Handbook (U.S. EPA, 2006) and produced a report from that peer review.2 Industrial
Economics Inc. selected five peer reviewers (Dr. Dallas Burtraw, Dr. Seth Blumsack, Dr. James
Bushnell, Dr. Frank Felder, And Frances Wood) who have extensive expertise in energy policy,
power sector modeling and economics to review the EPA Version 6 Reference Case and provide
feedback. The panel focused on the latest available Reference Case version and its
documentation at that time (May 2019 Reference Case).

Peer review panel has been asked to:

• Evaluate the suitability and scientific basis of the methods (model formulation), model
assumptions, model outputs, and conclusions derived from the model;

1	EPA periodically publishes updated projections and their documentation. Documentation, input and output files for

the latest EPA v6 Reference Case using IPM and links to the previous versions are located at
https://www.epa.gov/airmarkets/power-sector-modeling

2	https://www.epa.gov/airmarkets/ipm-peer-reviews-and-responses

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Identify specific strengths, weaknesses, limitations, and errors in the model
formulation, model assumptions, model outputs, and conclusions derived;

•	Propose specific options for correcting errors and fixing or mitigating weaknesses and
limitations in the model formulation, model assumptions, model outputs, and
conclusions derived;

•	Check the appropriateness of the set of model-scenarios for addressing uncertainty in

potential future power-sector trends and of particular relevance to future power sector
emissions.

The peer reviewers evaluated the adequacy of the framework, assumptions, and supporting
data used in the EPA Version 6 Reference Case using IPM, and they suggested potential
improvements. Overall, the panel found much to commend EPA; stating that the modeling
platform:

•	lends itself well to EPA analyses of air policy focused on the power sector

•	includes significant detail related to electricity supply and demand

•	includes data-rich representation both across different geographic areas and across
time

•	provides a reasonable representation of power sector operations, generating
technologies, emissions performance and controls, and markets for fuels used by the
power sector

•	is well suited to assess the costs and emissions impacts

•	documentation is well written, clearly organized, and detailed in its presentation of
most model characteristics

The independent peer review panel provided expert feedback on whether the analytical
framework, assumptions and applications of data in the Version 6 Reference Case using IPM are
sufficient for the EPA's needs in estimating the economic and emissions impacts associated
with the power sector due to emissions policy alternatives. The panel made recommendations
to improve the model's ability to represent the ongoing evolution of the industry; in particular:

•	Continued penetration of renewables

•	Increasing developments in energy storage technologies and markets

•	Changes in load shapes from new forms of demand, like electric vehicles

•	Evolving state and regional policies

•	Evolving ISO/RTO market rules

•	Increasing need for and advances in modeling capabilities of temporal resolution
Executive summary recommendations included:

1. Clarify types of uncertainty that the model is capable of handling

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2.	Reconsider coal plant turndowns and addition of operating reserves

3.	Consider incorporating upstream emissions

4.	Distinguish investment decisions between utility and merchant power plants

5.	Address the evolving gas markets regionalization and emerging sectors

6.	Consider alternatives to the current load duration curves

7.	Improve representation of behind-the-meter generation

8.	Increase transparency of retail pricing results

9.	Consider improvements in the representation of various policy mechanisms

10.	More thorough citing of sources and expanded explanations in documentation

Body of the Peer Review Report included over 100 recommendations (of which most of them
tied back to the Executive Summary Recommendations) and about 50 edits to documentation.
For quick and easy reference, all of the Peer Review Report recommendations and EPA's
responses to those are tabulated in the Appendix and also referenced to the Section 2 of this
document (EPA's response to Peer Review Report) for narrated responses.

Section 2 of this document provides a high-level response to the Executive Summary
recommendations of the Peer Review Report, where we also grouped, incorporated and
addressed many of the recommendations included elsewhere in the Peer Review Report.

Before and after Peer Review Panel completed their work, EPA published five updated v6
Reference Cases; namely May 2018, November 2018, May 2019, January 2020, and Summer
2021 Reference Cases. Vast majority of the Peer Review Panel recommendations, both in terms
of capability improvements and documentation, have been addressed in the last public release
with the Summer 2021 Reference Case (published in September 2021). EPA anticipates that
future updates will continue to improve some existing features and will introduce new
capabilities, as well as more detailed documentation as needed EPA is also working on
publishing a number of side cases with alternative set of assumptions.

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SECTION 2

ADDRESSING MAIN RECOMMENDATIONS

2.1	Updates to model to improve the model's ability to represent the ongoing evolution of
the industry: demand/supply, new technologies, transmission, evolving state and regional
policies, and ISO/RTO market rules

EPA continuously evaluates and makes updates or improvements to the model capabilities,
parametrization heuristics, input data, and assumptions. Some of these are routine updates
that are updated with every new reference case (such as the fleet information), some are
integrated as new data becomes available (such as demand, generation cost and performance
assumptions), and some categories are specifically evaluated as they become more prominent
and potentially impacting projections through emerging future power sector dynamics and
policy. EPA's reference case reflects on the books state and regional policies, and relevant
ISO/RTO market rules. In addition, model has existing and potential capabilities for various
possible policy mechanisms. Documentation of these capabilities, are usually not part of the
Reference Cases but are routine part of the incremental documentation or Technical Support
Documentation that accompanies policy or scenario analysis. Appendix of this document gives a
detailed account of such capabilities mentioned in the Peer Review Report.

2.2	Types of uncertainty that the model handles

EPA primarily focuses on a central "reference case", which highlights conditions that can be
reasonably expected. In order to evaluate how key uncertainties impact model projections, EPA
has previously released (incremental to May 2018 Reference Case)3 and plans to release
(incremental to Summer 2021 Reference Case) a range of scenarios that outline a
representative cone of outcomes. These scenarios will estimate the impact of changing natural
gas prices, renewable technology costs, and demand.

2.3	Coal plant turndowns, operating reserves, continued penetration of renewables,
dispatch

EPA models the turndown rate for coal plants at the unit level. The unit level turndown
percentages for coal units were estimated based on a review of recent hourly Air Markets
Program Data where most of the coal capacity has a turndown rate between 40% and 60%. EPA
believes having unit-specific turndown rate is beneficial to our model projections because it
accounts for the variation in performance of coal plants rather than representing it as a single
value for the entire fleet, which is the approach employed by many other power sector models.
EPA's turndown approach is an aspect of the model that we have revisited regularly and expect

3 https://www.epa.gov/power-sector-modeling/results-using-epas-power-sector-modeling-platform-v6-may-2018

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to continue to do so in the future, given that load following behavior has recently become more
common in the coal-fired fleet.

EPA has evaluated the inclusion of operating reserve constraints in IPM through a variety of test
runs and determined them to be beneficial for the projections, particularly for scenarios with a
high deployment of renewable resources. At this time, EPA does not believe additional reserve
products beyond operating reserve are necessary but will continue to evaluate this moving
forward.

2.4	Incorporating upstream emissions

It is important for EPA to maintain the ability to show emissions from the combustion of the
fuel and emissions specifically occurring at the power plant stack. This is central to both air
quality modeling efforts and the majority of EPA EGU rulemakings that regulate stack
emissions.

At the same time, EPA is developing approaches for quantifying upstream methane and C02
emissions associated with the extraction, production, and distribution of coal, oil, and gas used
in the power sector. EPA will include and document such data in relevant future applications.

2.5	Investment decision-making of utility and merchant power plants and capacity markets

While new build financing assumptions are not differentiated based on utility/merchant
categorization, retrofits do include this differentiation. This in turn results in more realistic
retrofit/retirement decisions for the existing fleet.

Within a cost minimizing framework assuming differentiated financing for new builds would
result in possible over-builds and under-builds as a result of effective differences in levelized
costs. Based on prior runs, these builds may be unrealistic in their concentrations. Instead, IPM
assumes a weighted average financing charge for all new builds of a given technology type.

Based on prior testing we believe the current approach, i.e. differentiated financing for retrofits
and weighted average financing for new builds is the most reasonable modeling convention.

2.6	Gas markets and natural gas price

Comments in this area tended to focus on two areas: 1) more transparency in documentation,
2) more definition given to under what scenarios EPA would reconstitute its natural gas supply
curves.

In regard to the former, EPA has supplemented the documentation with additional language
regarding the LNG export volume, non-power sector demand assumptions (particularly how it is

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accounting for significant changes in the petro-chemical industry), and the relationship
between GMM and IPM oil price assumptions. This is somewhat similar to the basin-specific
discussion included in the coal supply section (except that gas supply curves are national in
scope and the gas supply implementation is different from the coal supply implementation)
where EPA provides detail on mining techniques, market conditions, and geological factors that
are basin specific and experiencing change.

The appropriateness of the natural gas demand projected by IPM and the supply curves used in
the model are considered throughout scenario production. In each run, EPA evaluates
consistency of projected natural gas consumption and production with the basis differentials
provided by GMM. EPA will continue to document information concerning the incorporation of
GMM outputs in IPM analyses.

2.7	Alternative load duration curves changes in load shapes from new forms of demand (such
as electric vehicles); regional and temporal resolution

As an input to the model, the impact of alternative load shapes has been tested in a number of
scenarios and applications. For example, EPA is working on an analysis to support the
evaluation of impacts of warming temperatures on the power sector in the USA using IPM and
IPCC scenarios. This side case will demonstrate and quantify incremental impacts relative to the
EPA's reference case, taking into consideration impacts on electricity demand, power plant
capacity, power plant heat rates, transmission capacity and hydropower impacts, in addition to
identifying additional areas and improvements needed for further study. EPA has also
completed a number of internal analyses evaluating the impact of electric vehicle charging load,
varying both its magnitude and timing. Since the model's input structure allows to modify load
(both its shape and magnitude) as needed, we have evaluated various Energy Efficiency cases in
the past and will continue to do so.

IPM can be configured with varying number of seasons. For example, in v6, a winter shoulder
season was added to better capture seasonality in wind generation. The load segments can also
be customized to account for time of day to better capture solar generation. The seasonal
structure and segmental configuration is reviewed with each update and might need to be
revised in the future to capture electric vehicle load.

2.8	Improving representation of behind-the-meter generation

To improve the representation of behind-the-meter generation, EPA has recently updated its
approach so that non-dispatchable distributed generation affects the shape of the load
duration curve, instead of simply reducing the net energy for demand used in the projection.

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2.9	Increasing transparency of retail pricing model

EPA is improving the documentation for the Retail Price Model by providing further clarification
on and discussion of key components of the model. Additional improvements to the
documentation will also include an enhanced discussion of the purpose of the model, and
explain how that relates to the different methodologies for estimating retail price in
competitive and regulated regions.

2.10	Representation the of various policy mechanisms and publishing alternative/side cases

EPA has the capability to run a wide array of scenarios in IPM to inform and shed light on
important power sector projections. Previous iterations of IPM that have been released have
included alternative scenarios, for public dissemination and review. These scenarios have
included alternative assumptions for electric demand (high and low), renewable energy costs
(high and low), and natural gas price. EPA continues to consider, develop, and perform
alternative scenarios to inform its efforts to address pollution from the power sector, and will
continue such efforts. Where appropriate, EPA will release and disseminate scenarios to
accompany future IPM updates. In addition, EPA will consider such scenarios in other contexts
where IPM is being used, such as regulatory development.

2.11	Documentation improvements including results viewer

A number of documentation improvements were reflected in the Summer 2021 Reference Case
full-fledged documentation providing additional detail and clarity. These are tracked in the
Appendix table. Documentation updates will continue with each update as needed in light of
both formal reviews and comments received from stakeholder and user community.

EPA has refined the Results Viewer to make it more intuitive and easier to use. The controls
were modified to automatically match between primary and comparison cases to make use
easier. The units displayed above charts were updated to clearly indicate the cases being
compared. And finally, the "Read Me" guide was edited and updated for clarity.

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Appendix: Table for Detailed Accounting of Peer Review Recommendations and Narrated Responses

Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of renewable
industry

increases in the penetration of
renewables



2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of EF
adoption

changes in load shapes... [from] electric
vehicles



2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of storage
industry

changes in load shapes... [from] energy
storage



2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of state and
regional policies

state and regional policies



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of changes in
LDC

revising the intra-annual load segments



2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of modeling
for the power sector

solving the model chronologically



2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of modeling
for the power sector

solving a companion model that
describes chronological demand and
system operation using capacity
assumptions from IPM



2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of storage
industry

richer representation of energy storage



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.1

ES

ii

1

Consider changes to
the model formulation
that would improve
the model's ability to
represent the ongoing
evolution of the
industry

represent the ongoing
evolution of market
rules

incorporating changes in capacity
market rules into the model
(particularly as they relate to variable
renewable energy)



2.2

ES

ii

2

Clarify the types of
uncertainty that EPA's
Platform v6 is capable
of handling

Clarify the types of
uncertainty that are
not captured by the
model

documentation should provide guidance
to model users that more clearly
articulates the types of uncertainties
captured and not captured by the
model



2.2

ES

ii

2

Clarify the types of
uncertainty that EPA's
Platform v6 is capable
of handling

Clarify the types of
uncertainty and
address uncertainty in
a broader manner

consider evolution in the model
structure to address uncertainty in a
broader manner



2.3

ES

ii

3

Reconsider coal plant
turndown constraints
and possible addition
of operating reserves

Reconsider coal plant
turndown constraints
to determine if it
creates bias in coal
operations

EPA examine the turndown constraints
more closely to determine if they create
bias in coal plant operations, especially
in scenarios with low gas prices or high
renewable generation



2.3

ES

ii

3

Reconsider coal plant
turndown constraints
and possible addition
of operating reserves

Reconsider coal plant
turndown constraints
and consider operating
reserves as an
alternative solution

consider whether adding explicit
operating reserve requirements in the
dispatch would provide a better
representation of the impact of high
levels of renewable generators on the
grid



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.4

ES

iii

1

Consider
incorporating
upstream emissions in
addition to source-
level (power plant)
emissions

consider including
upstream emissions

consider including upstream emissions
in its reference case as a separately-
reported item (so upstream and stack
emissions are not combined together)



2.5

ES

iii

2

Distinguish between
investment decision-
making of utility and
merchant power
plants

Distinguish between
investment decision-
making of utility and
merchant power plants

Distinguish between investment
decision-making of utility and merchant
power plants



2.5

ES

iii

2

Distinguish between
investment decision-
making of utility and
merchant power
plants

Distinguish between
investment decision-
making of utility and
merchant power plants

evaluate whether a weighted average of
existing firms within a power region or
some other rule is a reasonable
representation of which type of firm is
more likely to make an incremental
investment



2.6

ES

iii

3

Address evolving gas
markets where Henry
Hub is less central to
pricing and where
emerging
petrochemical
production has
greater influence

Address evolving gas
market by describing in
the documentation the
model process for using
GMM

[Describe in the documentation the
model process for] iterating with the
Gas Market Model that generates the
natural gas supply curves and basis
differentials



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.6

ES

iii

3

Address evolving gas
markets where Henry
Hub is less central to
pricing and where
emerging
petrochemical
production has
greater influence

Address evolving gas
market by tracking
emerging

petrochemical sector

emerging petrochemical sector in the
Appalachian production region is likely
to affect regional natural gas pricing in
ways that may not be well represented
in the gas market model that EPA's
Platform v6 relies upon



2.7

ES

iii

4

Consider alternatives
to the current load
duration curves (LDCs)

Consider alternatives to
the LDC to better
account for inter-
regional trade

[How EPA] aggregates time into LDCs in
a way that... creates biases related to
the opportunities for inter-regional
trade



2.7

ES

iii

4

Consider alternatives
to the current load
duration curves (LDCs)

Consider alternatives to
the LDC

assess the trade-offs between different
approaches to aggregating load into
LDCs



2.8

ES

iv

1

Improve

representation of
behind-the-meter
generation

Improve representation
of behind-the-meter
generation

capture policies that encourage behind-
the-meter generation... [beyond]
represented as a change in demand



2.9

ES

iv

2

Increase transparency
of retail pricing results

Increase transparency
of retail pricing results

When EPA uses the RPM, we
recommend that the reporting of retail
rates be broken into component parts
so that the user can understand which
elements are endogenous to the model
and which are dominated by external
sources and assumptions



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.10

ES

iv

3

Consider

improvements in the
representation of
various policy
mechanisms

Improve representation
of policy mechanisms
such as dynamic
allocation of emission
credits

dynamic allocations within various
forms of emissions trading programs
such as output-based allocation under
cap and trade and a clean energy
standard



2.10

ES

iv

3

Consider

improvements in the
representation of
various policy
mechanisms

Improve representation
of policy mechanisms
such as EE
expenditures and
carbon pricing

expenditures on energy efficiency that
are linked to revenue from carbon
pricing



2.10

ES

iv

3

Consider

improvements in the
representation of
various policy
mechanisms

Improve representation
of policy mechanisms
such as flexible demand

ability to represent flexible demand that
may be encouraged at the retail level to
promote the integration of variable
renewable energy



2.11

ES

iv

4

More thorough citing
of sources and
expanded
explanations
throughout the EPA
Reference Case v6
documentation

Update the
documentation to
include the
development of the
load segments

development of load segments



2.11

ES

iv

4

More thorough citing
of sources and
expanded
explanations
throughout the EPA
Reference Case v6
documentation

Update the
documentation to
include treatment of
interregional trade

treatment of interregional trading



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.11

ES

iv

4

More thorough citing
of sources and
expanded
explanations
throughout the EPA
Reference Case v6
documentation

Update the
documentation to
include aggregation of
model plants

aggregation of individual plants to
model plants



2.11

ES

iv

4

More thorough citing
of sources and
expanded
explanations
throughout the EPA
Reference Case v6
documentation

Update the
documentation to
include more detail for
the retail price model

retail pricing model



2.1

2

2

3

Uncertainty

periodically review the
model to determine
whether model
structure should be
modified or
complemented with
other modeling
capabilities

EPA should periodically review the
model to determine whether EPA's
application of IPM model structure
should be modified or complemented
with other modeling capabilities

This is part of routine model development
process.

2.1

2

3

3

Chronological
modeling

restructure IPM as a
chronological model

restructuring IPM as a chronological
model

Possibility of making IPM a chronological
model is a significant task and may be
investigated. However, there is segmental
output information that can be used. In
addition, a production costing model such
as PROMOD can be used in conjunction
with IPM when required.

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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.1

2

3

3

Chronological
modeling

develop a companion
short-run chronological
model of system
operation

develop a companion short-run
chronological model of system
operation that would enable comparing
the outcomes of the model's load
duration curves with a more realistic
characterization of the temporal nature
of demand

ICF has run GE MAPS for EPA, while
performing analyses in support of the
MATS rulemaking, for example. ICF runs
PROMOD production costing model
routinely and could setup such a
framework if so desired by EPA. PROMOD
is a chronological model that can be run
annually and does not make investment
decisions. ICF runs PROMOD either at the
interconnect level or at a subset of an
interconnect level.

2.1/2.10

2

3

4

Demand response

incorporate demand
response

consider incorporating additional
factors into the model's formulation of
demand response [including]... changes
in total electricity consumption in
response to changes in price



2.1/2.10

2

3

4

Demand response

incorporate demand
alternatives/substitutio
ns to electricity

consider incorporating additional
factors into the model's formulation of
demand response [including]...
substitution between electricity and
other forms of energy consumption

This is not done through model
formulation. Gas power plants are a form
of substitution between electricity and
other forms of energy consumption. A
similar approach can be evaluated to
estimate a kWh to Btu relationship and
can be used in IPM.

2.1/2.10

2

3

4

Demand response

incorporate changes in
the load shapes

consider incorporating additional
factors into the model's formulation of
demand response [including]... changes
in the load shapes that will be observed
and projected under different scenarios

This is not done through model
formulation but load shapes are adjusted
based on scenarios evaluated.

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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.1/2.10

2

3

4

Demand response

incorporate variations
in supply-side short run
marginal costs (due to
increased VRE)

consider incorporating additional
factors into the model's formulation of
demand response [including]...
variations in supply-side short run
marginal costs (due to increased
penetration of variable renewable
energy)

In addition to the battery approach, we
could also utilize the DSM/EE option
functionality. NREL simulates flexible
demand/DR with a 100% efficient battery
that is time constrained. We can adopt a
similar approach in IPM to model DR
impacts under changing pricing patterns.

2.1/2.10

2

3

4

Demand response

incorporate retail TOD
pricing or retail pricing
linked to RE/clean
energy

consider incorporating additional
factors into the model's formulation of
demand response [including]...
potentially demand side retail prices
that vary by time of day or are linked to
resource availability directly require
cross-time-period analysis of electricity
demand

The endogenous demand response
capability allows us to estimate demand
response by load segment. In v6, we use
TOD based load segments and hence
demand response can indeed be linked to
TOD. Due to the TOD based load segment
structure, the generation from solar units,
for example, accounts for TOD. IPM is a
wholesale price model, which makes
linking to retail pricing very challenging.
We can make a simplification and allow
demand to move in response to wholesale
pricing.

2.7

2

3

5

Climate change
considerations

periodically evaluate
the model with respect
to weather
normalization of key
data inputs

recommend that EPA periodically
evaluate the model with respect to
weather normalization of key data
inputs

This has been evaluated in the past and
we will continue to do so.

2.7

2

3

5

Climate change
considerations

represent climate
change impacts in
generation

consider a more explicit representation
of climate change in the model's
specification of generation

On-going as scenario study.

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EPA's IPM Summer 2021 Reference Case
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2.7

2

3

5

Climate change
considerations

represent climate
change impacts in
transmission

consider a more explicit representation
of climate change in the model's
specification of... transmission

On-going as scenario study

2.7

2

3

5

Climate change
considerations

represent climate
change impacts in load

consider a more explicit representation
of climate change in the model's
specification of... load assumptions

On-going as scenario study

2.1

2

4

1

Transmission capacity

regularly revisit
implementation of
transmission

regularly revisit and, as appropriate,
revise EPA's implementation of
transmission outcomes and the
assumptions that shape anticipated
future transmission siting decisions

Transmission assumptions are regularly
updated in v6.

2.1

2

4

2

Storage

model energy storage,
including end-use
storage

rigorous treatment of energy storage
within the formulation of the model,
particularly with respect to the
opportunity to schedule demand and
achieve thermal and battery storage for
end-uses

Storage assumptions and parametrization
are regularly visited and updated as
needed in v6.

2.1

2

4

3

Capacity markets

represent resource
adequacy as they are
structured

representations of resource adequacy
requirements, as opposed to modeling a
generation reserve requirement

We will continue to monitor relevant
market developments and make
appropriate changes. The introduction of
the operating reserve constraint begins to
approximate this constraint.

2.11

2

4

4

Additional operational
constraint

include operating
reserve requirements

include operating reserve requirements

This is implemented. See Section 3.7

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EPA's IPM Summer 2021 Reference Case
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2.2

2

5

1

decision-maker
uncertainty

evaluate model results
in an option value
framework

improve the way they use model results
by explicitly considering them in an
option value framework

EPA has previously released and plans to
continue to release a range of scenarios
that outline a representative cone of
outcomes. These scenarios estimate the
impact of changing natural gas prices,
renewable technology costs, and demand.

2.11

2

5

2

runtime restrictions

publish runtime

restriction

requirements

any runtime restrictions required by the
EPA should be made explicit and used to
appropriately structure EPA's
application of IPM to the task at hand

This is a pragmatic preference rather than
restrictions.

2.10

3a

6

4

Demand

include electricity price
response in policy and
sensitivity cases where
prices vary significantly

We view the use of fixed electricity
demands without response to electricity
prices as problematic in policy and
sensitivity cases where prices vary
significantly from the Reference Case.
We recommend that EPA use this
feature when analyzing policy scenarios
that have significant price impacts
(perhaps roughly greater than 20%
variation in wholesale prices).

The capacity to perform demand response
already exists. EPA has used IPM's
demand response functionality while
conducting carbon policy analyses in the
past.

2.10

3a

6

4

Demand

publish in more detail
how the elasticity is
applied when used

recommend that the EPA Reference
Case v6 documentation describe in
more detail how the elasticity is applied
when used

When a certain parameter/capability is
used, they are always documented in the
corresponding side/alternative case or
policy case.

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EPA's IPM Summer 2021 Reference Case
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2.1

3a

7

2

Demand

develop better load
shapes over time

a more systematic way is needed to
develop load shapes over time rather
than just using a single metric of load
factors from ES&D or the AEO to shift
the curves

Usually, load factors are the only piece of
data that is available from AEO and NERC
projections. If future year load shapes that
underlie AEO or NERC demand projections
are available (for the use in side cases
possibly), then we can develop a
methodology to use those load shapes.

2.7

3a

7

4

Demand

evaluate using data for
a single year vs. a
multi-year average or
weather normalization
would be more
appropriate

recommend that EPA consider whether
using data for a single year creates any
biases and whether a multi-year
average or weather normalization
would be more appropriate

Both approaches could have pros and
cons for the various EPA applications
(including AQM). Using a multi-year
average could result in load shapes that
are very different from the original load
shapes and is not considered at this time.

2.11

3a

7

4

Overall

have consistency
among AEO vintages
used for data
assumptions

have consistency among AEO vintages
used for data assumptions

This is a goal but is hard to implement in
practice as not all parameters are
available or updated in any given year.
AEO or other sources, we strive to
incorporate most recent data available
with significance with every update.
Inevitably, not all data categories will
reflect the same calendar year or vintage
in any given IPM version.

2.3

3a

8

3

Dispatch

allow steam plants to
shut down for lowest
load time segments
when they run at full
capacity during the
peak segment

it appears that steam plants would not
be able to shut down for any time
segments (such as segments with
lowest load) if they are expected to run
at full capacity during the peak
segment.

Our turndown approach is an aspect of
the model that we have revisited regularly
and expect to continue to do so in the
future. Turndown constraints can be
reconfigured to allow coal plants to shut
down at time of lowest load. However,
this change should be considered with
care as to disallow overoptimization
through cycling.

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EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.3

3a

8

3

Dispatch, turndown
rate

publish information on
dispatch by time
segment

output files from EPA's Platform v6 do
not include information on dispatch by
time segment

Dispatch by time segment is not available
to either the public or EPA

2.3

3a

8

4

Dispatch, turndown
rate

develop turndown
rates based on
technical operational
considerations rather
than historical
economic
circumstances

the turndown constraints vary
considerably by unit, and some are as
high as 80% with most of them between
40% and 60%. Because these values are
based on historical operations rather
than current or projected engineering
considerations, they may reflect
historical economic circumstances that
may not apply in the future

The turndown assumptions can be
updated based on current data to reflect
the current operating behavior of coal
plants. Our turndown approach is an
aspect of the model that we have revisited
regularly and expect to continue to do so
in the future. In addition, if the low gas
price environment persists, then the
assumptions could also be relaxed
(turndown targets lowered) to reflect
increased cycling.

2.3

3a

8

5

Dispatch, turndown
rate

examine the turndown
constraints for bias in
coal scenarios with low
gas prices or high
renewables

recommend that EPA examine the
turndown constraints more closely to
determine if they create bias in coal
plant operations, especially in scenarios
with low gas prices or high renewable
generation.

We are currently working on this.

2.1

3a

9

1

Dispatch

add operating reserve
requirements

consider whether adding explicit
operating reserve requirements in the
dispatch would provide a better
representation of the impact of high
levels of variable renewable energy

This feature is implemented in the current
platform. See Section 3.7

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EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.1?

3a

9

2

Dispatch

analyze historical
generation versus the
model patterns by time
period for hydro

consider analyzing historical generation
patterns versus the model patterns by
time period to assess whether EPA's
application of IPM is significantly
overoptimizing hydro generation

The concern about overoptimization is
primarily related to run-of-river hydro
units that do not have storage. In the
current update, we have aggregated run-
of-river hydro units separately and then
model their generation through a
generation profile based on recent
history. See Section 3.5.2

2.1

3a

9

4

Transmission

update transmission
loss assumptions

The application of a 2.4% transmission
loss to each interregional transfer
strikes us as high for the Eastern
Interconnect, especially given the size of
the model regions and hence relatively
short distances for many of these
transfers. For example, in NEMS a 2%
loss factor is assumed for transfers
between regions and there are fewer
regions.

We are currently evaluating this
recommendation and can easily
update/implement.

2.1

3a

9

5

Transmission

perform sensitivity
cases where
transmission capacity is
added

performing sensitivity cases in which
additional transmission capacity is
added exogenously

The recommendation is to perform
sensitivity analyses where we exogenously
add transmission capacity. We have
incorporated endogenous transmission
builds, this sensitivity analysis may be
unnecessary.

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EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.3

3a

10

3

Capacity Expansion -
Setting the Capacity
Targets

add reserve ramping
constraint

application of IPM may need to be
modified to reflect other capacity
requirements beyond a simple reserve
requirement and declining capacity
values for variable renewable capacity.
For example, it may be appropriate to
add an additional reserve constraint
requiring a percentage of capacity is
capable of meeting a certain ramping
capability

We monitor the electricity markets
continuously and make updates to the
model to be consistent with changes in
the markets. As the resource mix changes
and requirements like California's or other
mechanisms become more common, the
model will be updated accordingly to
account for the changing dynamics. A step
in the direction is the incorporation of the
operating reserves constraints in v6. We
do not believe additional reserve products
are necessary for the scenarios we are
currently pursuing but will continue to
evaluate this moving forward.

2.3

3a

11

2

Capacity Expansion -
Setting the Capacity
Targets

modify the short-term
supply cost adders for
capacity expansion

The cost adders to capacity expansion
costs when expansion is rapid... are
quite steep with roughly a 45% cost
penalty on the second step. It might be
better to have smaller initial steps with
smaller cost penalties for the second
step.

These constraints are applied to all new
plants for the 2021-2035 run years.
However, they usually get activated for
solar and wind builds in runs having
stringent RPS/CES standards. In EPA v6,
the short-term capital cost adders step
widths are from AEO. However, the
approaches differ from AEO in the sense
that in IPM we are not updating the step
widths to account for the IPM builds.

2.3

3a

12

2

Capacity Expansion -
Rating the Capacity of
Alternative Resources

update the solar
capacity credits to
latest AEO

if the solar capacity credits are still
benchmarked to those of the AEO2017,
as indicated in the documentation, this
should be revisited because the AEO
methodology and resulting credits for
solar have changed considerably since
the AEO2017 was published

Solar capacity credits are no longer being
benchmarked with the AEO version. See
Section 4.4.5

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EPA's IPM Summer 2021 Reference Case
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2.5

3a

12

2

Capacity Expansion -
Rating the Capacity of
Alternative Resources

examine capacity
market rules and
consider the
implications of non-
performance risk

we recommend that EPA examine the
capacity credit methodology as system
operators change their capacity market
rules and consider the implications of
non-performance risk

This is standard practice, although there is
a balance between chasing today's rules
versus the 'true' value, as understood by
the model. We will continue to monitor
the changing rules.

2.5

3a

12

3

Capacity Expansion -
Rating the Capacity of
Alternative Resources

account for demand
response and energy
efficiency in capacity
markets

worth noting that demand response and
energy efficiency are providing non-
trivial shares of total capacity and even
larger shares of new capacity in many
capacity markets

We are continuing to plan for how to
incorporate these resources into our
modeling projections.

2.1

3b

13

1

Storage

incorporate additional
storage technologies
into the model

recommends that EPA consider
incorporating additional storage
technologies into the model

Work is ongoing.

2.1

3b

13

1

Storage

regularly revisit energy
storage cost,
performance, and
market assumptions

because the technologies, cost
structure, performance, operating
strategies, market rules, and regulations
related to storage are rapidly changing,
EPA may need to regularly revisit the
model's representation of storage

Ongoing work. We routinely consider this
for all technologies including storage.

2.1

3b

13

2

Storage

update energy storage
technologies, costs,
and operational
assumptions regionally

consider regional variations in energy
storage technology, costs, and
operations

In the current version our implementation
has regional variations of cost and
capacity credit. See section 4.4.5

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EPA's IPM Summer 2021 Reference Case
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2.1

3b

13

3

Nuclear

consider more flexible
nuclear dispatch

consider more flexible nuclear dispatch
in EPA's application of IPM

Nuclear dispatch is already flexible and is
not hardwired. The reviewers appear to
suggest that we model nuclear O&M costs
as a function of the level of dispatch. EPA
is participating in inter-agency workgroups
to research and implement updates in
modeling as needed.

2.1

3b

13

4

Heat Rates

vary heat rates by
season and over time

recommend that the heat rates of
generating units in EPA's application of
IPM vary by season and perhaps over
time

Heat rates are less impacted than capacity
by change in temperature. This issue is
less important as compared with the
impact on capacity. We considered this in
the past but have not found value for our
applications so far. It might be interesting
to consider grid reliability / reserves in
light of units that might not be able to get
the cooling water they need and therefore
have to limit generation. But that would
be either more episodic and hard to
reflect in a long term capacity expansion
model or would be considered as a side
case evaluating warming impacts.

2.1

3b

14

2

Heat Rates

vary the available
capacity of a given unit
by season

recommend that EPA's application of
IPM vary the generation capacity of a
given unit by season, or add text to the
documentation explaining why seasonal
variation is not necessary

This primarily impacts CT and CC units.
The primary impact is we might be
underestimating generation potential in
the winter season. We will evaluate the
LOE required to implement this feature in
IPM.

2.7

3b

14

3

Generation
Assumptions

update generation over
time to account for
climate change

consider adjusting the EPA's Reference
Case generation assumptions over time
to account for climate change

This is a scenario case.

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2.1

3b

14

4

Generation
Assumptions

vary generation
assumptions by
market/regulatory
environment

consider varying some generation
assumptions by market/regulatory
environment

For existing units, EPA uses unit specific
heat rates, emission rates, and technology
assumptions. In addition, where possible,
unit and state level emission regulations
are also modeled in detail. Some of the
other assumptions such as unit level
availabilities can be used if such data is
available.

2.4

3c

15

1

Assignment and Scope
of Emissions Factors

document upstream air
emissions in fuels
prices or in generator
marginal costs

consider documenting how upstream
air emissions are reflected in fuels
prices or in generator marginal costs
within its Power Sector Modeling
Platform

Upstream air emissions can be estimated
through post processing. However, the
challenge will be in defining the scope of
what constitutes upstream and then
developing the associated emission
factors.

2.11

3c

15

3

Emission Control
Options

periodically review the
technology options for
emissions control

suggest that EPA periodically review the
technology options for emissions
control in EPA's application of IPM to
determine if this portion of the model
could be made simpler with the
reduction of emissions control
technologies from which modeled
plants can choose

This is always considered with major
updates.

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EPA's IPM Summer 2021 Reference Case
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2.11

3c

15

4

Emission Control Costs

publish the raw
engineering data used
to develop the unit cost
values

Chapter 5 of the EPA platform v6
documentation includes unit cost
estimates derived from the Sargent and
Lundy study but does not provide a
formal citation for the study or the raw
engineering data used to develop the
unit cost values. Publication of these
data would make the cost figures used
by EPA's Platform v6 more transparent
than they are currently. We recommend
that EPA consider the costs and benefits
of this additional data transparency as
weighed against the benefits of being
able to access and use proprietary data,
which in some cases may be more
granular or up-to-date than data
existing in the public domain.

As of 2022, we are working with S&L and
in the process of updating reports.

2.11

3c

16

1

Emission Control Costs

periodically compare
emissions control cost
data with publicly
available data

EPA should also periodically compare its
emissions control cost data with
relevant information that exists in the
public domain, such as the Integrated
Environmental Control Model (IECM)
developed by Carnegie-Mellon
University.

We will consider this.

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2.11

3c

16

2

Emission Control Costs

include natural gas
combined cycle plants
with carbon capture as
a capacity option

the option to choose natural gas
combined cycle plants with carbon
capture appears to be turned off within
the model... we recommend that EPA
restore this technology option under
relevant analyses.

These options are currently back in v6.

2.11

3c

16

3

Emission Control Costs

document interactions
between IPM and
GeoCAT

recommend that EPA incorporate
additional specificity... in the
documentation... [relating to] any
interactions between IPM and GeoCAT.

IPM and GeoCAT are never iterated
together, nor there are any interactions
between the two tools. Updated
documentation provides additional detail.
Please see Section 6.2

2.11

3c

16

4

Emission Control Costs

re-evaluate the oil price
assumption related to
EOR and the C02
storage cost curves

should re-evaluate the oil price
assumption related to EOR... [and] re-
evaluate the C02 storage cost curves

On-going work, we update oil prices
regularly.

2.11

3c

16

5

Emission Control Costs

remove C02 transport
pipeline economies of
scale and document
model approach

Some elements of the C02 transport
model are also not clear, particularly
related to the economies of scale in
pipeline transportation. The method
described in Section 6.3 of the
documentation appears to assume that
C02 sources that are transporting C02
over longer distances for long-term
geologic sequestration are taking
advantage of some undescribed scale
economies in the form of capacity
sharing in C02 pipelines.

In the latest reference case, EPA is no
longer accounting for scale economies
while estimating the cost of C02
transportation. Please see Section 6.3

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2.5

3d

17

5

Power Sector Finances
and Economics

add equation and
reference for the
capital charge rate

The description of the calculation of the
capital charge rate would be made
substantially more clear with an
equation. In particular, whether EPA's
Platform v6 uses the common "short
cut" version of the capital charge rate
(Stauffer, 2006) could be made more
clear

The reviewers indicated a desire to have
more information on the capital charge
rate and to ensure that the concerns of
Stauffer (2006) are not affecting the
capital charge rate. Stauffer, a founder of
ICF, indicates that there could be
confusion between real and nominal
capital charge rates and input parameters,
which is not a problem. He may have
indicated other concerns, but we have not
reviewed his 2006 article in detail. We
could review the article and determine
next steps, if any.

2.5

3d

17

6

Power Sector Finances
and Economics

describe the debt life
versus the asset life

recommend an explicit statement in the
documentation describing the debt life
versus the asset life.

In general, the debt life is shorter than
the book life. This is based on the tenure
of debt, especially in the IPP sector. See
Section 10.10.2

2.5

3d

17

7

Power Sector Finances
and Economics

update assumptions on
debt-to-equity ratios
and the cost of
merchant debt

assumptions on debt-to-equity ratios
and the cost of merchant debt, which in
the market environment at the time of
this writing may be high. EPA's Platform
v6 uses a value of 7.2%, but one of the
stated data sources for debt-to-equity
ratios currently suggests that the cost of
debt may be substantially lower.This is a
data point that we suggest be updated
in future revisions of EPA's Platform

Financial assumptions are regularly
updated, and D:E ratios are one of the
metrics we closely track.

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2.5

3d

18

2

Power Sector Finances
and Economics

use a different WACC
formula with a constant
leverage ratio

[Consider using a different WACC
formula other than Hamada] Brealy and
Myers (2011) point out that a constant
leverage ratio is a more realistic
assumption

The Hamada equation is used to adjust for
differences in the reported debt to equity
structure and the targeted structure. The
reviewers point to a source that they
assert favors a constant leverage
assumption. In the case of IPPs, there has
been very high debt shares, large amounts
of financial distress, especially in some
periods. Accordingly, we believe this
unusual situation warranted adjustments
to more sustainable debt levels.

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Power Sector Finances
and Economics

account for
differentiated risk
appetite of utility
versus merchant
investment costs of
capital

consider addressing this differentiated
risk appetite [of utility versus merchant
investment costs of capital] in future
versions of EPA's modeling platform.
One possibility would be to introduce
different hurdle rates for different
investor decision-makers and effectively
split investment decisions within EPA's
application of IPM.

While new build financing assumptions
are not differentiated based on
utility/merchant categorization, retrofits
do include this differentiation. This in turn
results in more realistic
retrofit/retirement decisions for the
existing fleet. Within a cost minimizing
framework assuming differentiated
financing for new builds would result in
possible over-builds and under-builds
because of effective differences in
levelized costs. Based on prior runs, these
builds may be unrealistic in their
concentrations. Instead, IPM assumes a
weighted average financing charge for all
new builds of a given technology type.

In the peer review, the issue that was
identified as the most important is the use
of a weighted average cost of capital of
regulated utilities and merchant
powerplants. In nominal terms, the
WACCs of utilities are 4.9% versus 6.7%
for IPPs; the weighted average is 5.6%.
The latest modeling bases its financial
assumptions on a 60:40 utility: merchant
weighting. The 60:40 weighting
approximately equals the 2015-2019
average for renewable and thermal
additions in the US. The concern is that
the use of the average may not
adequately characterize the financing
costs. The peer review suggests
designating some regions as regulated
utility and others as merchant IPP. The
decision to use an average was based in
part on the uncertainty about the
structure in the long term. The approach

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also reflects the concern that there could
be an unrealistic skewing of regional
results. Namely, low capital cost regions
would disproportionately make capital
investments including disproportionately
investing for export to high capital cost
regions.

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2.11

3d

19

4

Power Sector Finances
and Economics

update documentation
on tax credits for wind
energy

The documentation could also explain
more clearly how tax credits for wind
energy are treated.

The tax credits for both PTC and ITC
are modeled as a reduction in the
levelized capital costs of those resources.
We provided better documentation.

2.11

3e

20

7

Coal

update documentation
on coal mine closures

there is not enough information
provided in the documentation to
discern whether coal mine closures are
exogenous or endogenous within the
model and the degree to which closures
in the model reflect recent changes in
regional fuel supplies



2.11

3e

21

2

Coal

evaluate differences
between ElA's and
EPA's coal

prices/supply to ensure
consistence across
other sector demands

Because the AEO2017 view of coal
prices and supplies reflected in export
and non-electric sector demand may
not match EPA's view of coal prices and
supply, the projections of other sector
demands and exports may be
inconsistent with power plant demand.

We acknowledge that there may be
inconsistencies in our current approach.
There will always be seams between IPM
and AEO, we will continue to investigate
to limit them and their impact.

2.11

3e

21

2

Coal

keep the base
projections for coal up
to date

consider keeping the base projections
up to date (using AEO2018 (or AE02020
if an update is done) versus AEO2017)

This is always considered and usually
implemented at every update.

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2.6

3e

21

4

Natural Gas

run the GMM and IPM
iteratively when
necessary

One disadvantage of this static curve
approach is that it treats prices in
different years as independent in EPA's
Platform v6 context, rather than as a
function of cumulative production that
may vary by EPA scenario, even though
the underlying curves were developed
with that consideration by GMM. This
can be addressed by re-estimating the
curves by running the models
iteratively, as in the Reference Case set-
up, when it seems necessary due to
significant changes in gas demand.

While IPM's endogenous gas model can
address this issue, an alternate approach
is to regenerate the gas supply curves
whenever there is significant divergence
in the gas demand relative to that in the
reference case. An initial Ref Case is set up
by iterating between GMM and IPM. But
we do check when/if the static curves are
no longer appropriate for a given case.

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2.6

3e

21

4

Natural Gas

publish methodology
for deriving gas supply
curves

recommend that EPA publish more
information about the methodology for
deriving the curves

The slopes of the gas supply curves are
derived based on ICF's assessment of
change in natural gas prices historically
based on several parameters like rig
count, production, etc. and certain
assumptions of the natural gas resource
base moving forward to determine the
short-term and long-term supply elasticity
that feed into the supply curves. The way
the supply curves are built is that they are
more elastic over time compared to the
short-term elasticity as the resource base
can respond to price changes. In other
words, the short-term elasticity is higher
than the long-term elasticity. More
elaborate documentation is provided. See
Section 8.2.1

2.6

3e

22

1

Natural Gas

describe how LNG
exports are determined

It is also not clear the degree to which
LNG exports, both export capacity
expansion and utilization, are
determined endogenously versus
predetermined.

ICF assumption of LNG exports for EPA
base case is exogenous; however, GMM
has the capability to change the LNG
exports over time in response to change in
natural gas prices. More elaborate
documentation is provided. See Section
8.3.5

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2.6

3e

22

2

Natural Gas

update seasonal gas
price differentials
across scenarios

The GMM also serves as the basis for
seasonal price differentials that capture
the difference between the Henry Hub
price and gas prices in model regions.
While these differentials are
endogenously projected by GMM with
variable costs as a function of pipeline
throughput and pipeline capacity
expansions, they are fixed in a given
scenario context.

Under scenarios with major changes in
natural gas demand regionally, the change
in basis can be captured by GMM based
on the pipeline infrastructure build-out
necessary to support the demand growth
under that particular scenario. However,
this requires iterations between GMM and
IPM.

2.6

3e

22

3

Natural Gas

include petrochemical
sector demand in the
GMM

Within the GMM, econometric
equations project other sectoral
regional gas demands. The elasticity of
these demands presumably impacts the
overall supply elasticity of gas to the
power sector. We note, however, that
an emerging petrochemical sector in the
Appalachian production region is likely
to affect regional natural gas pricing in
ways that may not be well represented
in the gas market model.

GMM base case forecast for EPA base case
projects significant growth in natural gas
production from the Marcellus and Utica
region from 2019 through 2050 (about 25
Billion Cubic Feet per Day) which does
account for growth in NGL demand and
exports from the Appalachia region
exogenously.

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2.6

3e

22

5

Other Fuels

ensure consistency
across oil price
assumptions between
IPM and GMM

oil prices are treated inconsistently
across EPA's Platform v6 and ICF's GMM
platforms. While oil prices for power
generation are based on the AEO2017,
diesel fuel prices used in developing rail
rates for coal are from the AEO2016. At
the same time, oil prices used in the
GMM, which are used to determine fuel
switching in the industrial sector, are
quite different from those from the AEO
that are used in the rest of EPA's
Platform v6

In the future reference cases, DFO and
RFO fuel prices will be made consistent
with the crude oil price projections used in
the GMM.

2.1

3e

23

4

Renewable Resources

apply generic
transmission costs to all
units including wind
and solar

It would seem more consistent for the
generic transmission network costs to
be applied to all units rather than
exempting wind and solar. Otherwise
this provides a bias towards wind and
solar PV development

These costs are currently applied in the
v6. Documentation incorporated better
explanation of distance to transmission vs.
generic transmission network costs,
aligning NRELand AEO approach as much
as possible. Please see Section 4.4.2

2.7

3f

24

5

Regional and
Temporal Resolution

evaluate differences in
peak load and peak
net-load

Load aggregation can dilute outcomes
that are concentrated into a small
number of hours... EPA's Platform v6
addresses this well by specifying a very
high peak load segment, representing
only 1% of all hours. However, key
transient outcomes in the system may
not be limited to only peak hours,
particularly with extensive adoption of
renewable energy resources.

We will investigate this in the near future.

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2.7

3f

24

6

Regional and
Temporal Resolution

evaluate load
aggregation
implications regarding
inter-regional trade

Load aggregation necessitates difficult
modeling choices regarding inter-
regional trade... diagnose the full
impacts of this implementation. Our
intuition is that it constitutes a hidden
penalty on trade between regions; in
order to export during hours in which
trade is beneficial, the model may be
forcing additional trade in hours in
which trade is not beneficial. If true, this
means the model will bias downward
trade between regions.

The intuition is correct. There could be
hours when power might be exported
during hours when it might not be
needed. Additional analysis is not required
to confirm this assessment.

2.7

3f

26

4

Regional and
Temporal Resolution

document interregional
trade

One additional comment on this point is
that the documentation does not
describe this aspect of interregional
trade.A description with an
accompanying example would help
promote understanding of this feature
of the model



2.7

3f

26

5

Regional and
Temporal Resolution

evaluate aggregating
load over a larger
geography

Geographic aggregation involves trade-
offs between accuracy over time vs.
space... One way to reduce the
problems identified above [related to
inter-regional trade] is to aggregate
over larger geography.

We will investigate this in the near future.

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2.7

3f

27

1

Regional and
Temporal Resolution

evaluate the model's
ability to represent
regulations focused on
peak or episodic
emissions

Load aggregation limits modeling of
inter-temporal constraints... For
regulations that concern total output or
emissions from a power plant during a
season or year, the aggregation is likely
relatively benign. However, for the
purposes of assessing any
environmental regulations focused on
peak emissions, episodic emissions, or
emissions intensity, the aggregation
could be more problematic.

This will be considered in the future if
such policy design is necessary.

2.7

3f

27

4

Regional and
Temporal Resolution

Publish model outputs
by load-segment

Publish more output details: Currently
model outputs are not broken out by
load-segment. This additional output
detail may allow stakeholders to better
judge the relative impacts of the various
aggregation assumptions in a given
policy context

Dispatch by time segment is not available
to either the public or EPA.

Duplicate with row 55

2.7

3f

27

5

Regional and
Temporal Resolution

evaluate tradeoffs
between regional and
temporal aggregations

Investigate the Time vs. Geography
Trade-off: It is possible that the goals of
the model may be better implemented
with more temporal resolution and that
this could be aided by less geographic
resolution



2.7

3f

28

2

Regional and
Temporal Resolution

evaluate grouping
hours first by time of
day and then by load
segment

Consider grouping hours first by time of
day and then by load segment, instead
of the other way around.

The current approach was implemented
for simplicity. The alternate approach can
also be implemented. Such an approach
will eliminate the possibility of load
segments having zero hours.

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2.7

3f

28

3

Regional and
Temporal Resolution

evaluate grouping
hours first by load
segment for a whole
interconnection and
then by region

Investigate the implications of grouping
hours first by load segment for a whole
interconnection and then by region...
group hours by their interconnection-
wide load level and then subdivide into
regions. For example, the top 37
summer hours would be chosen from
the hours with the highest total load
across the WECC.

We will investigate this in the near future.

2.7

3f

28

4

Regional and
Temporal Resolution

evaluate grouping
hours into time-of-day
blocks (e.g., 4 hours)
and model them
sequentially

Represent time as a sequence of "model
hours" or "model days." ... One
alternative would be to group hours
into time-of-day blocks (e.g., 4 hours)
and model them sequentially, allowing
for better representation of some inter-
temporal constraints, inter-regional
trade, and probably renewable energy
and storage output. One such "model
week" per season could capture a peak
day and other important load
characteristics.

A sequential hour approach may not work
in models that are based on a load
duration curve. Needs further evaluation.

2.7

3f

28

5

Regional and
Temporal Resolution

evaluate grouping
hours into time-of-day
blocks for typical
weekdays and weekend
days with a
preservation of peak
loads through a peak-
day or other method

Represent time as a sequence of "model
hours" or "model days." ... Another
alternative would be to group hours
into time-of-day blocks for typical
weekdays and weekend days with a
preservation of peak loads through a
peak-day or other method.

IPM has the capability to separate load
segments based on weekday and
weekend days in addition to TOD. We
have performed some test runs. This
functionality can double the number of
load segments.

2.7

3f

28

6

Regional and
Temporal Resolution

link the model results
with a dispatch model

Run the output of a model scenario
through a more detailed dispatch
model.



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2.7

3f

29

2

Regional and
Temporal Resolution

model fewer future
years to compensate
for more detail within a
given model year

Model fewer future years. One way to
compensate for more detail within a
given model year would be to run fewer
model years. Seven, instead of eight,
explicit model years would reduce the
number of demand segments (region +
hours).

Outputs serve multiple purposes of EPA
applications and we do consider output
years carefully. The future run years in
five-year increments are also important
due to significant reductions in new unit
costs and the start of several state level
clean energy standards.

2.5

3f

29

3

Regional and
Temporal Resolution

evaluate using a higher
discount rate in the
objective function

Consider the impact of the discount rate
in the objective function... An even
higher discount rate may be appropriate
to minimize the impact of out-year
decision making on model outcomes

We use discount rates based on our
financial analyses. Further thought needs
to be given in regards to use of discount
rates whose primary function is to reduce
the impact of out years on model
outcomes. Previously we used a post-
processing tool to change policy cost NPV
with different discount rate, not in the
objective function, but it is a tool for
evaluation.

2.10

3g

29

5

emerging policy and
industry issues to
consider

model dynamic
allocation of emissions
allowances in cap and
trade programs

Although trading programs are
represented well in EPA's Platform v6,
the documentation indicates that the
model does not include any explicit
assumptions on the allocation of
emission allowances among model
plants under any of the programs. An
element of cap and trade that may be
challenging to model is dynamic
allocation of emissions allowances that
maintains the emissions cap.

IPM has the capability to model output-
based allowance allocations methods and
has performed such analyses in the past.
However, there may not be an immediate
need for this functionality. The cap and
trade programs promulgated by EPA do
not account for this policy lever; it is not
one of the central policy parameters
under discussion, and is not utilized
anywhere at the moment (including
RGGI).

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2.10

3g

30

2

emerging policy and
industry issues to
consider

model clean energy
standards with
effective emissions
targets that adjust over
time in response to the
quantity of production

challenges arise in representing clean
energy standards, which are emissions
intensity standards with effective
emissions targets that adjust over time
in response to the quantity of
production.

These constraints can be approximately
modeled through a set of two constraints
in IPM. Constraint 1 can model the
emission intensity standards through
Ibs/MWh constraints and Constraint 2 can
model the effective emissions targets
through cap based constraints. We are
currently exploring issues related to CES
policy design.

2.10

3g

30

3

emerging policy and
industry issues to
consider

model dynamic
allocation of emissions
allowances in cap and
trade programs

Other challenging elements in
representing power sector
environmental policies include dynamic
adjustments to emissions budgets
based on the prevailing price in an
auction, as illustrated by the emissions
containment reserve in the Regional
Greenhouse Gas Initiative



2.10

3g

30

5

emerging policy and
industry issues to
consider

document the
interactions between
electricity

sales/transmission and
renewable energy
credit markets

there is an interaction between
electricity sales and transmission, and
renewable energy credit markets.
Although we understand that this
interaction is embodied in the model,
we have not seen it represented in
previous exercises of the model or
described in the documentation

IPM solves for the power, fuels, and
environmental markets simultaneously.
The interaction among these markets and
within these markets are modeled
endogenously in an integrated manner.
We provided further detail in
documentation. Please see Section 2.3.10

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2.10

3g

31

1

emerging policy and
industry issues to
consider

evaluate leakage risk
between RPS policies
and carbon pricing
policies

Policies such as carbon pricing that
promote an increase in renewable
generation in one region could
precipitate a decrease in renewable
generation in another region if
renewable energy credits become
available in the region introducing
carbon pricing that can be used for
compliance with renewable portfolio
standards in other jurisdictions.

Such an analysis may only be relevant
when EPA is designing or promulgating
any of these policies. When necessary,
leakage issues will be addressed in policy
contexts in new analyses or rulemakings
where this is relevant.

2.10

3g

31

2

emerging policy and
industry issues to
consider

evaluate impact of the
New Source Review in
constraining existing
generation and limiting
new investments

Some prescriptive policies such as New
Source Review constrain the utilization
of an existing generating unit and limit
investments in new units in a
geographic area. The Agency should pay
special attention to this in evaluating its
modeling

As part of the flat file generation process,
emissions from new units are not assigned
to areas which are non-compliant. This
approach can work in instances where
only a subset of an IPM region is affected
by these requirements. However, if an
entire region is affected by these
restrictions, then we may need to disallow
the build of such units in those regions.

2.10

3g

31

3

emerging policy and
industry issues to
consider

model state level
policies that encourage
behind-the-meter
generation

The model seems to capture policies
that affect the bulk power system - but
does not seem to capture state level
policies that encourage behind-the-
meter generation except represented as
a change in demand.

The model could be developed and
enhanced to do this kind of analyses,
however this is not our priority currently.
We can address this in other ways using a
more simplified approach. This is
something we would model separately
and provide it as an input into IPM.

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2.10

3g

31

4

emerging policy and
industry issues to
consider

account for MOPR rules
impact on nuclear and
capacity market
compliance

if EPA models nuclear generation
incentives from state-level zero-
emission-credit (ZEC) policies, it would
also need to evaluate whether those
nuclear plans should count towards
satisfying a regional capacity constraint.
Under final MOPR rules, which are as of
yet to be determined, such nuclear
capacity may not be part of capacity
market compliance

Once the final rules are known, such units
can be provided with zero capacity credit.

2.10

3g

32

2

emerging policy and
industry issues to
consider

improve the
representation of the
C02 emissions rate for
imports to California

one last finding pertains to the
representation of the C02 emissions
rate for imports to California, at 0.428
MT/MWh... A careful solution to this
could be found through iteration,
solving the model twice varying the
level of demand in California in order to
identify the marginal resource providing
power to the state and region, but this
may require additional Agency
resources.

The approach implemented was a tradeoff
to minimize complexity. Potential
approaches can be investigated to better
represent AB 32. One potential solution is
to focus more on the recent CA clean
energy and RE requirements. However, it's
not clear to identify a good path towards
modeling imports into CA. We will
continue to work on the methods for how
to improve upon our current approach.

2.9

3h

33

1

Retail price estimates

document the purpose
of the NUG adder in
RPM

While it is not obvious that the capital
costs of a merchant NUG would be
directly passed on to retail rates, we
assume the NUG adder is included
because these costs are captured in
long-term contracts between the
generator and the local load-serving
entity (but this is not explained in the
documentation)

We will include this in the documentation.

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Documentation is available here

2.9

3h

35

1

Retail price estimates

document the purpose
of the NUG adder in
RPM

The general structure of the generation
pricing formulas seems appropriate, but
the purpose and magnitude of
elements, such as the NUG adder,
should be better explained.

We will provide better documentation

2.9

3h

35

2

Retail price estimates

define the difference
between competitive
vs. regulated regions

The logic behind the definition of
competitive vs. regulated regions is
unclear. There are many possible
definitions of "regulated" and
"competitive" and the RPM utilizes
definitions from ElA's Annual Energy
Outlook for its assignments of regions
to these categories. This may not be the
best definition for this application.

We will provide better documentation

2.9

3h

35

4

Retail price estimates

publish more of RPM
results and their
components

Based on the above comments, we
recommend that EPA improve
transparency of the RPM results and
their components... One suggestion
would either be a table or stacked bar
chart detailing not just the total rate (or
change in rate) but also the components
that make up that total. Most of these
details are available but take
considerable effort to put together.

We consider RPM as a first order price
generation tool. It is also used more for
estimating the change in prices rather the
absolute level of prices. Providing retail
price components might be confusing and
a digression. Provided better
documentation and disaggregated
impacts.

2.9

3h

73

1

Retail price estimates

define the difference
between competitive
vs. regulated regions

EPA should evaluate and articulate the
purpose of distinguishing between
competitive and regulated regions



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Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.9

3h

37

2

Retail price estimates

consider regression
analysis for estimating
the retail rate

Consider a simpler retail price formula
based upon regression analysis of the
relationship between generation costs
and retail rates over time.

The purpose of the RPM is to measure the
impact of a policy on prices.

2.2

4

38

4

non-parametric
uncertainty

show how behavior
may change or may
depart from expected
net present value
maximization in the
presence of uncertainty

one limitation of the focus on
parametric uncertainty is that sensitivity
analysis does not show how behavior
may change or may depart from
expected net present value
maximization in the presence of
uncertainty

Investment decisions can be impacted
under uncertainty. If the intent is to create
a strategy that is robust across a range of
futures, then we can evaluate an
approach such as a stochastic LP that can
generate robust results under a range of
scenarios. Additionally, this does not have
to be analyzed through IPM development
but a conceptual or weight-of-evidence
response. We have been evaluating this
for retirements.

2.2

4

39

1

non-parametric
uncertainty

adjust the hurdle rate
for investment and
retirement options to
account for option
theory

option theory suggests rational decision
makers will delay irreversible
investments (and retirements) in the
face of uncertainty to gain more
information about the uncertain aspects
of the scenario. This behavior will not
be evident in an inter-temporal
optimization linear program such as
IPM. However, this element of decision-
making under uncertainty might be
represented by adjusting the hurdle
rate for investment and retirement
options, perhaps implemented as a
shadow cost of capital for investments
that would be vulnerable to specific
parametric uncertainty.

This does not have to be evaluated
through IPM development but a
conceptual or weight-of-evidence
response.

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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.2

4

39

3

parametric
uncertainty

publish which
parameters or
combinations of
parameters most
heavily influence model
outputs

Beyond the scenario runs made public
by EPA, it is not clear what sensitivity
analyses EPA conducts to determine
which parameters are the most
important in determining variation in
model outputs. EPA's application of IPM
is so complex that it may be the case
that no single parameter is driving the
model outputs all by itself. Some
attempt at investigating and publishing
which parameters or combinations of
parameters most heavily influence
model outputs in the Reference Case
would be very useful.

Having methodical and documented
sensitivity runs when we go through the
development phase would be a very costly
and time-consuming undertaking. We do
this on an ad-hoc basis (dozens of
sensitivities are run/tested); and many
times we do not obtain the full outputs of
test runs (as they are not necessarily fully
QA'd) but assess what the results
directionally suggest. Also, not all of those
sensitivities can be planned beforehand
but as the need emerges (in conjunction
to other updates being made). Best
method would be to envisage/group these
runs retrospectively after we have arrived
at a reference case. This would still render
significant additional effort but it would
be a more concise and targeted work
serving documentation purposes and
justifying various assumptions/updates
made. We will consider this when we have
resources.

2.2

4

40

1

parametric

uncertainty,

loadshapes

model scenario that
includes changes in the
shape of the LDC from
vehicle electrification

Changes in the shape of the load
duration curve: (1) vehicle
electrification

This is ongoing work.

2.2

4

40

1

parametric

uncertainty,

loadshapes

model scenario that
includes changes in the
shape of the LDC from
TOD pricing

Changes in the shape of the load
duration curve: (2) time-varying retail
rates that encourage load shifting and
peak-time demand response,



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Response
Document
Section
where
addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.2

4

40

1

parametric

uncertainty,

loadshapes

model scenario that
includes changes in the
shape of the LDC from
demand response

Changes in the shape of the load
duration curve: (3) wholesale
(aggregated or individual customer)
demand response that is generally
dispatched during summer peaks to
ameliorate very high market clearing
prices or reduce peak system loadings
for reliability reasons

Ongoing work. In the past we added
demand response in for meeting capacity
markets.

2.2

4

40

1

parametric

uncertainty,

loadshapes

model scenario that
includes changes in the
shape of the LDC from
behind-the-meter
generation and energy
storage

Changes in the shape of the load
duration curve: (4) the penetration of
behind-the-meter generation and
energy storage.

We made adjustments to the LDC for
distributed solar PV and implemented.
When there is an EPA outlook/expectation
we can consider this for other distributed
technologies.

2.2

4

40

3

parametric

uncertainty,

loadshapes

model scenario with
negative demand
growth from EE

Even without changing the load
duration curve, we also suggest
including a scenario in EPA's Platform,
along with the Reference Case, that
involves negative demand growth
arising through greater energy
efficiency measures for buildings and
appliances

We can execute a first order estimate run,
assuming the load shape doesn't change
overtime. However, a more realistic
approach would require more work.

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Response
Document
Section
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addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.2/2.10

4

41

1

parametric
uncertainty, fuel
supply

model scenario
involving negative
shocks to fuel supplies

encourage EPA to publish scenarios
alongside the Reference Case involving
negative shocks to fuel supplies,
particularly in the northeastern U.S.
where resistance to additional fuel
delivery infrastructure has been high.
These negative shocks could be
modeled as outages or de-rates to
certain types of generating units in
certain regions within EPA's application
of IPM, or (perhaps preferably) using
high fuel prices to indicate shortage (see
an example for natural gas in Bent, et
al., 2018).

These can be modelled either by changing
fuel prices exogenously or through a full-
scale iteration with GMM.

2.2/2.10

4

41

3

multiple parametric
changes

model combo scenarios
that interact shifts in
LDC with existing
parametric scenarios
(such as low/high gas
prices and renewable
costs)

Scenarios that interact shifts in load
duration curves with existing parametric
scenarios (such as low/high gas prices
and renewable energy costs)

We can do this if needed, deemed
valuable and priority. LDC runs could be
tested when we have resources.

2.10

4

41

4

multiple parametric
changes

model combo scenarios
involving very low gas
prices and low
renewables costs

Scenarios involving very low gas prices
and rapidly declining capital costs for
renewable power generation

We can do this if needed and if deemed
valuable and priority. We are posting two
alternative reference case runs.

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Response
Document
Section
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addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.10

4

41

5

multiple parametric
changes

model combo scenarios
involving fuel supply
shocks and low
renewable costs

Scenarios involving fuel supply shocks
and low capital costs for renewable
power generation (implying a larger
dependence on renewable energy
during supply shocks, and the response
of the system to that known
dependence)

We can do this if needed, deemed
valuable and priority. We are posting two
alternative reference case runs.

2.10

4

41

6

parametric
uncertainty,
unexpected events

model parametric
surprise events

we observe that EPA's Platform v6 as
currently configured is ill-equipped to
handle unexpected events that might
arise over the multi-decadal time frame
that it models... however, we do see a
straightforward way for EPA to be able
to model specific scenarios that involve
parametric surprise events, and
encourage EPA to publish the results of
such scenarios alongside the Reference
Case

EPA has performed such analyses in the
past. We can do this if needed, deemed
valuable and priority.

2.10

5

43

4

policy analysis

model policies or
technologies that
endogenously shift load
across time

policies or technologies that
endogenously shift load across time
would introduce challenges and may
not be achievable given the current
model configuration, as we understand
it, except through an iteration
procedure.



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Response
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addressed

PR

Sect.
#

PR
Page
#

PR
Para.
#

PR Recommendation
Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.10

5

44

1

policy analysis

model energy efficiency
and improve demand
representation

Because of the various federal proposals
to promote energy efficiency, EPA may
need to revisit its representation of
demand in order to be useful to analysis
of these policies.

Energy efficiency can be modeled
explicitly in IPM and has been done in the
past. The level of detail can be at the
measure level.

2.10

5

44

2

policy analysis

model state policies
governing retail tariffs,
including payments for
DG, electrification, and
shifting demand to
align with VREs

One of the largest challenges for EPA
going forward may be the
representation of policies at the state
level governing retail tariffs, including
payments for distributed generation,
and incentives to promote
electrification that may intentionally
align demand growth with the
availability of variable renewable energy
resources

Demand side policy representation will
have to follow an updated approach to
representing demand that doesn't rely
solely on EIA data. This would be a phase
two of any demand work we would
execute. We are developing in-house
capabilities to run NEMS.

2.10

5

44

3

policy analysis

model retail TOD prices
or retail RE prices

a possibly important policy mechanism
in the next decade is the determination
of retail prices that are differentiated by
time or type of electricity use



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#

PR
Page
#

PR
Para.
#

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PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.10

5

44

3

policy analysis

model time varying
prices applied to new
sources of
electrification

However, potentially more important
are time varying prices applied to new
sources of electricity demand such as
electric vehicles, water heating, and
building heating that embody
technologies with inherent storage
capability. These types of electricity
uses do not require all the attributes of
typical "instant on" electricity use.
Consequently, they may not be priced
at the same level and they may not be
burdened with the sunk costs
associated with the reliability aspects of
the existing grid, and retail prices may
be adjusted accordingly

Managed charging essentially addresses
this as we have been working on. For a
more comprehensive approach, we would
need to develop an EPA approach to
modeling demand before we can start
modeling cases like this in IPM.

2.10

5

44

4

policy analysis

model time-varying
prices including cross-
time-period elasticities
of electricity use and a
demand side model

To represent the meaningful aspects of
time-varying prices requires cross-time-
period elasticities of electricity use
within a fully functioning demand side
model.

IPM's DSM/EE modeling capability can be
exercised to model some of the demand-
side optionalities available in the market.
However, we do not plan to have a fully
functional demand-side model in the
near-term.

2.10

5

44

5

policy analysis

account for the effects
of uncertainty on
economic behavior

Another potentially important limitation
of EPA's policy analyses (that we also
raise in the context of EPA's Platform v6
representation of baseline uncertainty)
is the model's ability to account for the
effects of uncertainty on economic
behavior

We have been doing analytical work on
retirements outside of IPM to address
this.

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#

PR
Page
#

PR
Para.
#

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PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.11

6

46

3

model documentation

update documentation
on developing load
segments

Development of load segments: The
process used for developing load
segments as described in the
documentation is unclear.

The documentation is already clear.

2.11

6

46

4

model documentation

update documentation
on treatment of
interregional trading

Treatment of interregional trading: The
documentation's description of inter-
regional trade, especially related to the
load segments, is not very clear. The
documentation indicates that trade is
modeled on a seasonal basis, yet it is
our understanding after discussions
with EPA that trade is modeled by load
segment.



2.11

6

46

5

model documentation

update documentation
on aggregation of
model plants

Aggregation of model plants: The
documentation's description of the
aggregation of model plants also
requires clarification..., it is our
understanding that fossil units are
aggregated no further than at the plant
level

Section 4.2.6 documentation is already
clear.

2.11

6

46

6

model documentation

improve the
publication of data
tables on the EPA
website

Publication of data tables on the EPA
website: The use of tables uploaded
directly to the web is understandably
necessary given the large size of many
of the data inputs. However, a few
improvements are suggested.

The list of tables posted separately are
listed at the end of each chapter.

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PR
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#

PR
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#

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Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.11

6

47

2

model documentation

include in the
documentation a more
complete description of
which AEO case for
what

Guide to EPA's Platform v6 Output Files:
It would be helpful to include a
reference in section 2.5.2 of the
documentation to the output file guide
that is on EPA's website. In addition,
when ElA's AEO cases are used to set up
alternative sensitivity cases, a more
complete description of which AEO case
is being used and what inputs are being
used from the case would be helpful.

So Far EPA has always used AEO reference
cases. If and when a different AEO case or
alternative demand cases are used, these
will be appropriately documented.

2.11

6

47

5

results viewer

insert a few
clarifications in the
READ ME instructions
for the Results Viewer

To avoid user confusion, we would
recommend that EPA insert a few
clarifications in the READ ME
instructions.

Addressed.

2.11

6

47

6

results viewer

update Results
Viewer's distinction
between "plant type"
and "plant category"

We found the Results Viewer's
distinction between "plant type" and
"plant category" confusing. For
example, it is unclear what a user
should choose for nuclear plant type.
The readme tab indicates that plant
type and plant category may be merged
in the future, and we agree this would
be clearer.

Revised.

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#

PR
Page
#

PR
Para.
#

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Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.11

6

47

7

results viewer

update Results Viewer
so that the displayed
results indicate the
cases being compared

The displayed results should indicate
the cases being compared (i.e., the
difference between what to what) and
the units of measure reflected in the
results. The readme tab indicates that
the results represent "changes from the
comparison model," but it would be
helpful to include this on the graphics
page accompanying the map.

Addressed.

2.11

6

47

8

results viewer

Make more intuitive
the "comparison case"
for other metrics, such
as capacity factors and
emissions rates

The use of the "comparison case" for
other metrics, such as capacity factors
and emissions rates, is clever but not
very intuitive.

Already limited the dropdowns to be
active when absolutely necessary and to
automatically match the Primary Case
selections where it makes sense to do so.

The Results Viewer is squeezed for screen
real estate, so the popup box seems like
the best way to give users a handy cheat
sheet (rather than permanently displaying
it)

2.11

6

48

2

results viewer

allow map sheet to
display two sets of
absolute values

In the map sheet, the comparison
functionality is confusing and only
works for displaying differences, rather
than two sets of absolute values.

While the display could be altered to show
this, the challenge is that displaying two
numbers per state would become illegible
(either too small a font or overlapping
values). The whisker chart is an alternate
graphing method that can fill a user's
need.

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Sect.
#

PR
Page
#

PR
Para.
#

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Section/Category

PR Recommendation
Summary

Detailed Recommendation Text

Additional EPA Response Notes
(detailed narratives start after Executive
Summary rows)

EPA's IPM Summer 2021 Reference Case
Documentation is available here

2.9

6

48

4

retail price model
documentation

update the discussion
of utility depreciation
costs

In the discussion of utility depreciation
costs, the units are mills/kWh but these
are not defined by year. In addition, the
"directly from" is not explained
sufficiently as to whether the reader can
find these in a published document or
table or whether this was provided by
EIA

This will be addressed when an updated
RPM documentation published.

2.9

6

48

5

retail price model
documentation

update documentation
with additional detail
on the NUG adder and
the regional tax rates

The documentation would benefit from
additional detail for the non-utility
generators (NUG) adder and the
regional tax rates used in the RPM.

This will be addressed when an updated
RPM documentation published.

2.9

6

48

6

retail price model
documentation

define regional tax
dollars

Also related to regional tax rates, it is
not clear what is included in "regional
tax dollars" referenced in the
documentation.

This will be addressed when an updated
RPM documentation published.

2.9

6

48

7

retail price model
documentation

describe how the
percentage of each
region that is
deregulated or
regulated were derived

Attachment 1 of the documentation
includes a table showing the percentage
of each region that is deregulated or
regulated. We recommend that EPA
describe how the percentages were
derived, rather than simply citing the
AEO.

This will be addressed when an updated
RPM documentation published.

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