Control of Emissions From New Highway Vehicles and Engines; Guidance on EPA's Certification Requirements for Heavy-Duty Diesel Engines Using Selective Catalytic Reduction Technology, 32886-32896 [2011-13851]
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[FR Doc. 2011–13928 Filed 6–6–11; 8:45 am]
BILLING CODE 4830–01–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 86
[FRL–9315–2]
Control of Emissions From New
Highway Vehicles and Engines;
Guidance on EPA’s Certification
Requirements for Heavy-Duty Diesel
Engines Using Selective Catalytic
Reduction Technology
Environmental Protection
Agency (EPA).
ACTION: Request for comments.
AGENCY:
EPA is requesting comment
on draft guidance and related
interpretations concerning the
application of certain emission
certification regulations to those onhighway heavy-duty diesel engines that
are using selective catalytic reduction
systems to meet Federal emission
standards. EPA will review the
comments and provide final guidance
and interpretations in a future Federal
Register document.
DATES: Any party may submit written
comments by July 7, 2011.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2010–0444, by one of the
following methods:
• On-line at https://
www.regulations.gov: Follow the on-line
instructions for submitting comments.
• E-mail: a-and-r-docket@epa.gov.
• Fax: (202) 566–1741.
• Mail: Air and Radiation Docket,
Docket ID No. EPA–HQ–OAR–2010–
0444, Environmental Protection Agency,
Mailcode: 6102T, 1200 Pennsylvania
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SUMMARY:
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Avenue, NW., Washington, DC 20460.
Please include a total of two copies.
• Hand Delivery: EPA Docket Center,
Public Reading Room, EPA West
Building, Room 3334, 1301 Constitution
Avenue, NW., Washington, DC 20460.
Such deliveries are only accepted
during the Docket’s normal hours of
operation, and special arrangements
should be made for deliveries of boxed
information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2010–
0444. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through https://
www.regulations.gov your e-mail
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses. For additional information
about EPA’s public docket, visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
For additional instructions on
submitting comments, go to ‘‘What
Should I Consider as I Prepare My
Comments for EPA?’’
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
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materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Air and Radiation Docket, EPA/DC,
EPA West, Room 3334, 1301
Constitution Ave., NW., Washington,
DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
Docket is (202) 566–1742.
FOR FURTHER INFORMATION CONTACT: Greg
Orehowsky, Heavy-Duty and Nonroad
Engine Group, Compliance and
Innovative Strategies Division, Office of
Transportation and Air Quality, U.S.
Environmental Protection Agency; 1200
Pennsylvania Avenue, (6405J), NW.,
Washington, DC 20460. Telephone
number: 202–343–9292; Fax number:
202–343–2804; E-mail address:
Orehowsky.Gregory@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Purpose
This Federal Register document
describes and seeks public comment on
draft guidance for complying with
adjustable parameter regulations at 40
CFR 86.094–22 as they apply to
certification of on-highway heavy-duty
diesel engines using selective catalytic
reduction (SCR) technology to meet
emission standards for oxides of
nitrogen (NOX). This draft guidance
includes EPA’s interpretation of
relevant regulatory provisions in light of
available information on current and
developing approaches for effective SCR
controls. After considering any public
comments received, EPA will issue the
guidance and interpretations in the
Federal Register, and will use them in
reviewing any application for
certification application involving SCR
received on or after the effective date of
the guidance. The draft guidance
contained in this document reflects the
fact that manufacturers of heavy-duty
engines and operators of trucks have
gained significant experience in the
design and use of SCR systems for these
engines, and this experience should be
reflected in the certification process. We
invite public comment on the draft
guidance and interpretations set forth
below.
Until the effective date of the final
guidance and interpretations,
manufacturers should continue to refer
to the regulations and the existing
guidance documents noted below and to
work with their certification
representatives. We recognize that SCR
technology will continue to mature, and
we anticipate that appropriate designs
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for heavy-duty diesel vehicles and
heavy-duty diesel engines using SCR
systems may continue to evolve as
additional experience with the
technology is gained.
This draft document provides specific
examples of how we interpret existing
certification regulations and how we
intend to apply these regulations to
heavy-duty diesel engines using SCR
systems, based on the information
available to us. These examples are not
exclusive and are to be considered
examples. Manufacturers remain able to
present their own unique strategies that
are not the same as the examples we are
providing, and such strategies will
remain subject to our review and
approval under the certification
regulations. Manufacturers must still
show EPA that they meet all statutory
and regulatory requirements when they
apply for certification.
II. Overview
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In promulgating the 0.20 gram per
brake horsepower-hour NOX standard
for 2010 model year heavy-duty diesel
engines, based on a specified regulatory
test procedure, EPA recognized SCR
technology as one potential approach
for achieving the required emission
reductions. EPA identified several
issues for manufacturers to address in
developing and applying SCR
technology. Those issues related largely
to the technology’s use of a chemical
reducing agent to reduce NOX
emissions. The reductant is generally in
liquid form, which is referred to in this
document as DEF (‘‘diesel exhaust
fluid’’). DEF is stored in a tank located
on the vehicle and is injected into the
exhaust downstream of the engine. SCR
technologies require drivers to refill
DEF on a regular basis and are
dependent on appropriately broad
availability of DEF.1 EPA regulations
governing certification of engines
generally require manufacturers to show
that emission control technologies are
adequately designed to limit
adjustments that may increase
emissions (‘‘adjustable parameters,’’
discussed in detail below). SCR is
unique among emission controls in that
it requires on-going driver interaction to
ensure proper operation of the system.
1 A Class 8 truck equipped with standard dual
150-gallon fuel tanks can travel approximately
3,600 miles between DEF tank refills, assuming a
20-gallon DEF tank and representative DEF dosing
rate of 3 percent of fuel usage. DEF price varies
depending on whether it is supplied via bulk
container (commonly used by fleets and growing
numbers of truck stops) or a 1 to 2.5-gallon jug.
Current prices for bulk DEF at a truck stop are
generally less than $3.00 per gallon and jug prices
can be $4.00 or more per gallon.
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To comply with the NOX standard,
most heavy-duty engine manufacturers
developed SCR systems because of their
high efficiency in reducing NOX
emissions. A relatively unsophisticated
SCR system can achieve 60 percent
reduction and a robust system can
achieve greater than 80 percent
reduction. This enables engine
calibrations that increase fuel economy.
Additionally, SCR technology has a
relatively lower cost compared to NOX
adsorber technology.
In developing SCR systems,
manufacturers consulted with EPA
about how SCR systems could be
designed and what other steps would be
needed (e.g., concerning DEF
availability) to allow SCR to be used
consistent with EPA regulations. Over a
period of years, EPA has developed and
refined guidance to address how
manufacturers could effectively address
issues related to compliance with the
regulations for adjustable parameters.
Manufacturers have addressed the
adjustable parameter regulations by
designing engines that employ warning
systems for the driver and engine
operation-related inducements for
drivers to refill DEF tanks with proper
DEF.
Manufacturers have also worked to
increase DEF availability through
infrastructure development. DEF
infrastructure and sales volume have
continued to grow since introduction of
2010 model year trucks equipped with
SCR systems. Initially, DEF availability
was concentrated around major truck
routes, but has since increased in areas
away from these locations. DEF is now
available for sale in every state at truck
stops and service facilities, and is
available for delivery to fleet locations,
as well. To assist drivers in finding DEF,
multiple Internet-based DEF locator
services have also been developed. Sales
volumes of DEF are increasing
significantly and are believed to
correlate with the increased delivery
and use of SCR equipped trucks.
Increasing demand supported by sales
volume should continue to drive the
expanding infrastructure.
III. Relevant Regulatory Provisions
Under Section 203(a)(1) of the Clean
Air Act, engines and/or vehicles must
be certified as conforming with all
applicable regulations before they may
be introduced into commerce. Of
particular relevance for on-highway
heavy-duty diesel engines using SCR
technology are the provisions that
govern adjustable parameters at 40 CFR
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86.094–22.2 In particular, 40 CFR
86.094–22(e) authorizes EPA to
determine those vehicle or engine
parameters that will be subject to
adjustment for emission testing
purposes, and 40 CFR 86.094–22(e)(1)
discusses how the Agency determines
which parameters are subject to
adjustment.
It is important for manufacturers to
control the emissions performance of an
engine or vehicle over the full range of
any adjustable parameter in order to
ensure that in-use operation is as good
as projected at the time of certification.
When emission-related parameters can
be adjusted, there is a concern that the
engine or vehicle can be operated at
settings other than the manufacturer’s
recommended setting, possibly
increasing emission levels.
If a parameter is subject to
adjustment, the engine may be tested
over any point in the range of
adjustment and must meet the
emissions standard through the range of
adjustment. The Administrator
determines the range of adjustment for
emissions testing based on whether the
means used to inhibit improper
adjustment (e.g., limits, stops, seals) are
adequate. 40 CFR 86.094–22(e)(2) sets
forth how EPA determines the adequacy
of the limits, stops, seals or other means
used to inhibit improper adjustment.
For any parameter that is not adequately
limited, 40 CFR 86.094–22(e) authorizes
EPA to adjust the setting within the
physical limits or stops during
certification and other compliance
testing. If a parameter is determined to
be adequately inaccessible, sealed, or
otherwise inhibited from adjustment,
the vehicle will only be emission tested
at the actual settings to which the
parameter is adjusted during
production. 40 CFR 86.094–22(e)(2)(i)
and (ii) identifies certain types of
parameters subject to adjustment, and
identifies criteria related to technology,
time, or expense for determining
whether adjustment of the parameter is
adequately limited. These provisions
indicate that the technology used to
limit adjustment, or the burden on the
operator to make an adjustment (e.g.,
more than one-half hour in time or more
2 The regulatory provisions governing allowable
maintenance at 40 CFR 86.004–25 and 40 CFR
86.094–25, and auxiliary emission control devices,
or AECDs at 40 CFR 86.004–2, 40 CFR 86.082–2 and
40 CFR 86.004–16 are also relevant to certification
of engines using SCR technology, but are outside
the scope of this document. Manufacturers should
continue to refer to existing guidance noted below
covering these regulatory provisions.
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than $20.00 in cost),3 can be adequate to
determine that the parameter is
adequately limited and would not be
treated as adjustable outside of the
specified range for purposes of
emissions testing for compliance with
the standard. 40 CFR 86.094–22(e)(2)(iv)
states that in determining the adequacy
of a physical limit, stop, seal, or other
means used to inhibit adjustment of an
adjustable parameter, EPA will consider
the likelihood that settings other than
the manufacturer’s recommended
setting will occur during in-use
operation of the vehicle or engine,
considering such factors as, but not
limited to: (1) The difficulty and cost of
getting access to make an adjustment,
(2) the damage to the engine/vehicle if
an attempt is made, (3) the effect of
settings beyond the limits, stops, seals,
or other means on engine performance
characteristics other than emission
characteristics, and (4) surveillance
information from similar in-use vehicles
or engines.
The emission control efficiency of an
SCR system is highly dependent on the
presence and quality of the reducing
agent. Consequently, it is critical that a
SCR-equipped vehicle be designed so
that it is highly unlikely that the vehicle
will be used without proper reducing
agent. Given that most SCR system
designs store the required DEF in a tank
located on the vehicle and depend on
the vehicle operator to refill the tank
with DEF, EPA has indicated in
previous guidance that manufacturers
relying on SCR systems for emission
control must incorporate engine design
elements that make it highly unlikely
the vehicle will operate for any
substantial period without the
appropriate DEF. In practice, this has
meant designing engines or vehicles to
alert operators of when the engine will
run out of DEF, when the DEF is
inadequate, or if the SCR system is not
properly operating due to tampering or
some malfunction. This has also meant
designing engines or vehicles with
features that motivate operators to
ensure proper use of the SCR system,
such as engine derates and vehicle
speed inhibitors. Engine derates and
vehicle speed inhibitors alter important
vehicle performance characteristics,
such as acceleration, maximum vehicle
speed attainable, and ability to maintain
speed under various loads, that are
clearly noticeable to a driver.
3 This cost is represented in terms of 1978 dollars.
Adjusting for inflation, this would equate to
roughly $70.00 in 2011 dollars.
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IV. Prior Guidance
On March 27, 2007, EPA issued
guidance regarding the certification of
light-duty and heavy-duty motor
vehicles and heavy-duty motor vehicle
engines using SCR systems (CISD–07–
07).4 The purpose of the guidance was
to discuss EPA’s intended approach to
certification of engines using SCR
technologies and to facilitate
manufacturer planning in advance of
certification. EPA noted that several
regulatory requirements are uniquely
relevant to the certification and
implementation of engines using SCR,
specifically the regulatory provisions
dealing with allowable maintenance and
adjustable parameters. EPA suggested
that an SCR system that requires the
vehicle operator to replenish DEF
periodically is potentially an adjustable
parameter, and that unless operation of
the vehicle without DEF was
sufficiently inhibited through built-in
performance deterioration or some
similar system, vehicles using SCR
could be treated as having an adjustable
parameter range including no DEF in
the tank and could not be certified if the
vehicle would exceed emission
standards without DEF in the tank. EPA
provided guidance regarding how
engines using SCR could be designed
consistent with these regulatory
provisions to allow for certification of
such engines. EPA provided examples
of possible sufficient inducements,
including prohibiting operation if DEF
is not present and having vehicle
performance degraded in a manner that
would be safe but onerous enough to
discourage the user from operating the
vehicle until the DEF tank was refilled.
EPA also highlighted the need to assure
that DEF would be available and
accessible to operators and suggested
places where DEF could be made
available, such as dealerships and truck
stops. We recognized that SCR
technology was evolving and that our
guidance also might need to evolve.
On February 18, 2009, EPA issued
additional guidance (CISD–09–04) to
supplement CISD–07–07.5 This
guidance provided additional details
regarding certification of heavy-duty
engines with SCR systems. Particularly,
it outlined design elements that would
4 U.S. Environmental Protection Agency, Dear
Manufacturer Letter regarding ‘‘Certification
Procedure for Light-Duty and Heavy-Duty Diesel
Vehicles and Heavy-Duty Diesel Engines Using
Selective Catalytic Reduction (SCR) Technologies,’’
March 27, 2007, reference number CISD–07–07
(LDV/LDT/MDT/HDV/HDE), available at https://
iaspub.epa.gov/otaqpub/
display_file.jsp?docid=16677&flag=1.
5 See docket number EPA–HQ–OAR–2010–0444–
0018.
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make it highly likely operators would
replenish DEF prior to the tank being
empty and operators would not tamper
with SCR systems. The guidance
provided specific examples of robust
driver warnings and inducements to
help ensure operators addressed
conditions such as low reductant level,
improper reductant quality, and
tampered system components. EPA
continued to note the potential need for
additional guidance or changes in our
approach for SCR certification.
On December 30, 2009, EPA revised
CISD–09–04.6 The intent of this revision
was to clarify that CISD–09–04 was
guidance and did not set forth binding
requirements. EPA revised the guidance
and made clear that manufacturers
wishing to certify engines using SCR
technology should consult the revised
guidance document as well as the
guidance provided in CISD–07–07. EPA
also reminded manufacturers that they
should work with their certification
representatives to provide EPA adequate
descriptions of the strategies that are
incorporated in their SCR systems in
order to demonstrate compliance with
EPA’s certification requirements as set
forth in 40 CFR Part 86.
EPA has continued to monitor the
development of SCR technology and its
effectiveness in achieving emission
control in use. On July 20, 2010, in
conjunction with the California Air
Resources Board (CARB), we conducted
a public workshop to review existing
guidance and policies regarding design
and operation of SCR-equipped heavyduty diesel engines.7 In particular, EPA
reviewed approaches to designing SCRequipped engines to monitor and induce
appropriate responses to insufficient or
improper DEF, as well as strategies
regarding SCR systems that are
tampered with or defective. EPA
developed a strawman proposal
regarding future certification of heavyduty diesel engines equipped with SCR
technology,8 and opened a docket to
allow public comment regarding these
issues.9 As part of the strawman, EPA
included approaches for engines
6 U.S. Environmental Protection Agency, Dear
Manufacturer Letter regarding ‘‘Revised Guidance
for Certification of Heavy-Duty Diesel Engines
Using Selective Catalyst Reduction (SCR)
Technologies,’’ December 30, 2009, reference
number CISD–09–04 (HDDE), available at https://
iaspub.epa.gov/otaqpub/
display_file.jsp?docid=20532&flag=1.
7 See 75 FR 39251 (July 8, 2010).
8 See docket number EPA–HQ–OAR–2010–0444–
0016. The strawman proposal was not final
guidance.
9 See 75 FR 39251 (July 8, 2010). Public
comments received in response to the public
workshop are available in EPA’s docket EPA–HQ–
OAR–2010–0444, available at https://
www.regulations.gov.
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equipped with SCR, including designs
that monitor on-board DEF supply and
induce action to avoid low DEF supply
and operation with no DEF (or an
insufficient amount to allow proper
dosing). EPA also discussed detection of
poor quality DEF, as well as warnings
and inducements if poor quality DEF is
detected. In addition, EPA discussed
designs for engines equipped with SCR
systems to sufficiently reduce the
likelihood that SCR system operation
would be circumvented. EPA cautioned
manufacturers to review any element of
design that could be tampered with and
prevent proper operation of the SCR
system. Lastly, EPA noted DEF freeze
protection and infrastructure
requirements, and requirements
regarding unregulated pollutants.
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V. Experience to Date
A. EPA’s Certification Program
For the 2010 and 2011 model years,
EPA has certified a total of 71 onhighway heavy-duty diesel engine
families with SCR systems produced by
11 engine manufacturers. As part of the
certification process, engine
manufacturers are required to disclose
various aspects of the SCR system
designs, including elements of their
system that may be adjustable
parameters. To date, manufacturers’
designs have employed driver warnings
and inducements for low reductant
level, poor reductant quality, and
tampered or malfunctioning SCR
systems.
In order to ensure adequate
availability of DEF for use with
manufacturers’ engines, at the time of
certification EPA reviews
manufacturers’ plans for DEF
availability and accessibility. EPA
expects manufacturers to have DEF
available at their dealerships, to
encourage DEF availability at thirdparty locations, and to have an
emergency backup plan in case DEF is
not readily available.
When manufacturers implement new
emission controls, the engine
technology generally evolves and the
manufacturers make improvements over
the course of initial model years as they
develop and certify engines and
vehicles for each new model year. The
process of certification involves
interaction between manufacturers and
EPA technical staff about the nature and
effectiveness of emission controls and
often results in manufacturers
modifying emission control strategies
based on feedback from EPA. In the case
of SCR technology, manufacturers have
certified only a few model years of
engines that incorporate SCR
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technology, and EPA has seen maturing
approaches to implementing the
technology. For example, from the 2010
to 2011 model years manufacturers
improved or developed new engine/
vehicle diagnostic software that
provides more or better driver warnings
and inducements related to the SCR
system. Similarly, manufacturers are
also evaluating various sensors that are
expected to reduce the amount of time
necessary to detect poor quality DEF in
future model years. As with other new
engine technologies, defects in the
operation of SCR system strategies (e.g.,
driver inducements) are sometimes
discovered in the field, and
manufacturers initiate campaigns to fix
the issues and incorporate these fixes in
current and new model year production
engines.
B. California Air Resources Board SCR
Field Evaluation
The California Air Resources Board
(CARB) recently conducted field
investigations within the State of
California to evaluate implementation of
SCR technology for 2010 model year
vehicles.10 The investigations included:
(1) A survey of DEF availability, (2) a
survey to determine whether drivers are
using DEF or have tampered with SCR
components, (3) an evaluation of SCR
driver inducements, and (4) an
evaluation of the potential emissions
impact of improper SCR operation.
CARB conducted surveys of DEF
availability in March 2010 and August
2010. Both surveys indicated that DEF
is readily available at major diesel truck
stop refueling stations along major
interstate highways in California. In the
first survey DEF was determined to be
available at 85 percent of refueling
stations, and in the second survey DEF
was determined to be available at 92
percent of refueling stations. In
addition, both surveys indicated that 30
percent of retailers that normally supply
parts for heavy-duty vehicles have DEF
available. CARB noted that as older
engines are retired and an increasing
number of SCR-equipped engines enter
into operation, the availability of DEF
should increase with demand. It
concluded that DEF is currently being
offered in adequate supply for the
relatively limited number of vehicles
using SCR.
In September 2010, CARB conducted
random inspections of 69 trucks
equipped with 2010 model year engines
to determine whether DEF was being
10 California Air Resources Board, Report
regarding ‘‘Heavy-Duty Vehicle Selective Catalytic
Reduction Technology Field Evaluation,’’ May 2011,
available at https://www.arb.ca.gov/msprog/cihd/
cihd.htm.
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used, whether the DEF was of
appropriate quality, and whether driver
warning indicators (i.e., warning lights,
messages, or audible alarms) were
present. CARB found that all trucks
were using DEF and that the DEF was
of appropriate quality. No DEF-related
warning indicators were active and
there was no evidence of tampering
with SCR system components.
Additionally, CARB solicited
information from drivers about their
experience with locating DEF. Sixty
drivers indicated that they encountered
no problem locating DEF, while nine
indicated they had minor problems
locating DEF in California or in other
states. For those encountering problems,
the issue was limited to not being able
to purchase DEF at a particular refueling
station and instead having to purchase
it at a different refueling station. Sixtyeight drivers stated that they never ran
out of DEF while operating their
vehicles and only one driver indicated
that he drove for only 10 miles with an
empty DEF tank as indicated by the
driver’s gauge.
In the second half of 2010, CARB
conducted an evaluation of SCR
inducements on three trucks equipped
with 2010 model year engines and SCR
systems. The trucks evaluated were a
Freightliner Cascadia equipped with a
12.8-liter Detroit Diesel DD13 engine
(Test Vehicle 1), a Kenworth T800
equipped with a 14.9-liter Cummins ISX
engine (Test Vehicle 2), and a Dodge
5500 equipped with a 6.7-liter Cummins
ISB engine (Test Vehicle 3). Each truck
was operated under various test
conditions to observe the operation of
driver inducements and their
effectiveness in compelling the driver to
take a particular course of action. The
conditions under which the trucks were
operated included: (1) Operation until
the DEF tank was depleted, (2)
operation with water in the reductant
tank instead of DEF, and (3) operation
with a disabled DEF system. CARB staff
referenced the vehicle owner’s manuals
and the February 2009 EPA guidance to
ascertain the expected driver warning
indicators and inducement strategies
that were expected in each condition.
On Test Vehicle 1, the warnings and
inducements were implemented as
expected. CARB deemed the warnings
effective in drawing the driver’s
attention to the need for SCR-related
service. The initial inducement
incorporated in Test Vehicle 1 was a 25
percent engine torque derate and a 55
mph speed limitation. CARB concluded
that driving the truck with these
inducements was neither acceptable nor
tolerable, especially when trying to
accelerate or driving up-hill, and would
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likely cause a driver to refill with DEF
or correct the SCR problem as needed.
If the initial inducement were ignored,
the severe inducement incorporated in
Test Vehicle 1 was a 5 mph speed
limitation, which worked as designed.
The only way to resume normal
operation after the severe inducement
was to have the vehicle serviced by
draining the water out of the system,
filling the reductant tank with DEF, and
having the system reset by an
authorized service technician. CARB
determined that the inducements were
effective for this vehicle because the
constant inducement strategies and risk
of costly repairs would not be worth the
downtime and financial loss to the
business when DEF could simply have
been added to ensure proper vehicle
operation.
On Test Vehicles 2 and 3, the
warnings and some inducements were
implemented as expected, but certain
inducements were not. Test Vehicle 2
implemented the initial inducement (25
percent engine torque derate) in
response to DEF depletion, DEF
contamination, and DEF tampering
conditions, but failed to implement the
severe inducement (5 mph speed
limitation) in response to any of these
conditions. Test Vehicle 3 incorporates
an engine no-restart severe inducement
after a 500-mile to no-restart
countdown. After the 500-mile
countdown reaches zero and a safe
harbor event (key-off) is experienced,
the truck should not restart. The
inducement worked as expected in
response to DEF contamination and DEF
tampering conditions. In response to the
DEF depletion condition, Test Vehicle 3
started the 500-mile to no-restart
countdown as expected. However, after
the countdown reached zero and the
truck was shut off, the truck
successfully started the next day and
reset the countdown. On a subsequent
restart attempt after the countdown
reached zero, the truck successfully
implemented the no-restart condition.
CARB contacted Cummins, the engine
manufacturer for Test Vehicles 2 and 3,
about the failures. Cummins was aware
of and addressing the issues underlying
the failures. In the case of Test Vehicle
2, Cummins in the second quarter of
2010 had implemented a correction on
their engine production line and in the
third quarter of 2010 had begun a
voluntary recall of the engine family to
correct the problem.11 Similarly, in the
case of Test Vehicle 3, Cummins was
11 Voluntary recalls are a typical method for
manufacturers to remedy emission-related problems
they discover. Manufacturers are required to report
voluntary emission recalls to EPA and ARB, and
Cummins did so in this case.
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aware of a DEF heater malfunction that
contributed to the final inducement not
initiating as expected and was already
addressing the issue. CARB concluded
that for both Test Vehicles 2 and 3, the
warnings were deemed effective in
drawing the driver’s attention to the
need for SCR-related service. CARB also
concluded that the inducements on Test
Vehicle 2 were difficult to objectively
assess due to a malfunctioning throttle
position sensor that was encountered
during the testing. CARB concluded that
the inducements on Test Vehicle 3 were
effective once the DEF heater
malfunction was corrected.
C. American Trucking Associations
Survey
In 2010, the American Trucking
Associations (ATA) through its
technical advisory group conducted a
survey of 12 trucking fleets operating
across the United States regarding their
experience operating trucks with SCRequipped engines.12 The surveyed fleets
are some of the largest in the country
and operate an approximate total of
2,000 SCR-equipped trucks. The fleet
owners indicated that they would
probably purchase approximately 5,900
SCR-equipped trucks in 2011.
None of the surveyed fleets reported
any problems locating DEF and none
reported an engine derate, vehicle speed
limitation, or no-restart event caused by
operation with an empty DEF tank.
Similarly, no fleet reported issues with
the quality of DEF. There were six
reported instances of an engine derate
resulting from circumstances other than
an empty DEF tank. Two of these
instances were caused by
malfunctioning sensors and four were
caused by melted DEF supply hoses.
None of these instances were associated
with the behavior of the operator.
Survey respondents also reported a total
of five instances of NOX sensor
malfunctions, none of which were
related to driver tampering.13 ATA’s
fleet survey indicates that drivers do not
favor inducements involving an engine
power derate, especially if it occurs
while a truck under heavy load is
driving up-hill.
D. Cummins Survey
In 2010, Cummins collected
information from 47 different customerowned vehicles that were equipped
with Cummins 11.9-liter and 15-liter
12 See docket number EPA–HQ–OAR–2010–
0444–0019.
13 When a manufacturer determines that an
emission-related defect exists in 25 or more engines
of the same class or category and model year, they
are required to file an Emission Defect Information
Report in accordance with 40 CFR 85.1901 et seq.
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engines using SCR.14 The vehicles were
equipped with data-loggers that
wirelessly transmit data to Cummins
periodically on the operation of those
vehicles. At the time the data was
gathered, the vehicles had accumulated
a total of more than 2.4 million miles of
operation across the United States. For
approximately 99.7 percent of the
operating miles of the surveyed
vehicles, the DEF level was above 10
percent of tank capacity. For the
remainder of vehicle operation:
• DEF level was between 5 and 10
percent of tank capacity for less than
0.13 percent of the operating miles (i.e.,
approximately 3,000 miles).
• DEF level was between 2.5 and 5
percent of tank capacity for less than
0.03 percent of the operating miles (i.e.,
approximately 740 miles).
• DEF level was between zero and 2.5
percent of tank capacity (a condition at
which engines experienced derated
performance) for less than 0.04 percent
of the operating miles (i.e.,
approximately 920 miles).
• DEF level was at zero percent of
tank capacity (a condition at which
engines experienced derated
performance) for less than 0.02 percent
of the operating miles (i.e.,
approximately 520 miles).
In addition, DEF quality was
unacceptable (i.e., a faulted condition
existed) for less than 0.18 percent of the
operating miles (i.e., approximately
4,400 miles).
E. Navistar EnSIGHT Report
In 2010, Navistar retained EnSIGHT,
Inc. to test three 2010 model year SCRequipped trucks to analyze inducements
provided for in EPA certification
guidance.15 The following three trucks
were tested: (1) One Freightliner
Cascadia with a 15-liter Detroit Diesel
engine, (2) one Kenworth T–660 with a
15-liter Cummins ISX 15 435B engine,
and (3) one Dodge Ram 5500 crew cab
flatbed with a 6.7-liter Cummins ISB 6.7
305 engine. As part of testing, the three
trucks were operated with the intent of
circumventing the manufacturerdesigned inducements, which is in
contravention to EPA tampering
regulations.16
14 See docket number EPA–HQ–OAR–2010–
0444–0020.
15 See docket number EPA–HQ–OAR–2010–
0444–0015 for the August 2010 report. Navistar
provided EPA with supplemental details on the
August 2010 report in a follow-up October 2010
report. See docket number EPA–HQ–OAR–2010–
0444–0022 for the October 2010 report.
16 Section 203(a)(3) prohibits tampering with
emission controls. Such actions are illegal, unless
conducted as part of a testing program covered by
an Agency-issued testing exemption.
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Based on their testing program,
EnSIGHT reported the following:
• All trucks physically could be
operated for extended periods under an
initial inducement. Provided the driver
took particular actions, final
inducements could be avoided
indefinitely. For example, the
Freightliner Cascadia was driven over
1,000 miles on an empty DEF tank at a
limited speed of 55 mph, which is the
initial inducement. As long as no more
than 30 percent of the fuel tank capacity
(approximately 100 gallons) was added
at any single refueling event, the final
inducement, a 5 mph vehicle speed
limitation was not triggered. The
Kenworth T–660 was driven with an
empty DEF tank and a 25 percent engine
torque derate, which is the initial
inducement. As long as the engine was
not shut off for more than a few minutes
at a time, the 5 mph vehicle speed
limitation final inducement was not
triggered.
• When DEF tanks were empty and
water was added instead of DEF, two
trucks were able to run indefinitely.
When the Dodge 5500 was low on DEF
and began its 500-mile to final
inducement (i.e., no-restart condition)
countdown, the driver was able to fill
the DEF tank with water, start the truck,
and drive normally. This action cleared
the 500-mile countdown and the driver
display indicated a full DEF tank. On
one test run, the truck displayed visual
and audible warning signals after 73
miles of driving with water in the DEF
tank and eventually displayed the 500mile to no-restart countdown after 694
miles of driving. Upon shutting off the
truck after a total of 1,278 miles of
driving, a no-restart condition was
encountered. On a subsequent test run
with water in the DEF tank, the truck
was driven over 4,000 miles and
encountered no warning signals or
inducements. The Freightliner Cascadia
was driven over 15,000 miles with only
water in its DEF tank and triggered no
initial or final inducement.
• SCR system components could be
repeatedly disconnected and
reconnected to avoid particular
inducements. On the Dodge 5500, the
driver was able to disconnect the
injector electrical connector, which
would initiate a 500-mile to final
inducement (i.e., no-restart condition)
countdown. As the mileage countdown
continued, the driver could reconnect
the component and reset the 500-mile
countdown. On the Freightliner
Cascadia, when electrical connections to
the DEF injector, gauge, or tank pump
were unplugged, the truck was driven
for over 1,000 miles prior to triggering
an inducement.
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• Although the testing program was
designed to intentionally operate the
trucks until final inducements were
encountered, EnSIGHT also provided an
assessment of the impact of initial
inducements on driver behavior. They
concluded that a 25 percent engine
torque derate would not induce a
corrective response by the drivers,
including when the truck was fully
loaded. With this level of derate,
EnSIGHT’s drivers were able to operate
the Freightliner Cascadia and the
Kenworth T–660 at speeds up to 55 mph
and 65 mph, respectively. Of the
Kenworth T–660, EnSIGHT’s drivers
indicated that the truck could easily be
operated and was acceptable for typical
driving for long periods of time under
derate.
F. DEF Infrastructure and DEF Quality
The DEF infrastructure and sales
volume have continued to grow since
introduction of 2010 model year trucks
equipped with SCR systems. Initially,
DEF availability was concentrated
around major truck stops and truck
routes and 2.5-gallon jugs represented
the common mode of supply. Although
very limited, bulk DEF dispensing
typically utilized small storage tanks
located apart from the fuel islands at
truck stops. The refilling of fuel and
DEF tanks at truck stops was also more
likely to require two separate purchase
transactions.
The continually increasing DEF
infrastructure and sales volume have
resulted in improved DEF availability
along major truck routes as well as other
locations. ‘‘AdBlue and DEF Monitor,’’ a
publication of Integer Research, reports
that DEF is available for sale in jug form
in every state.17 Integer Research also
reports that DEF is available for delivery
to fleet locations in every state, as well.
To assist drivers in finding DEF,
multiple Internet-based DEF locator
services have been developed. One of
these services, DiscoverDEF.com, run by
Integer Research, recently announced
that DEF consumption in the U.S.
reached 2.3 million gallons per month
in December 2010 and that in August of
the same year consumption volumes
increased 43% compared to the
previous month. Also, a number of
suppliers reported sales volumes
doubling in September 2010 alone.
These increases in DEF consumption are
believed to correlate with the increased
delivery and use of SCR-equipped
trucks.
Increasing demand supported by sales
volume helps drive the continuing
17 See docket number EPA–HQ–OAR–2010–
0444–0021.
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expansion of DEF infrastructure. The
same locator service recently reported
that more than 100 truck stops in the
U.S. and Canada now have DEF
available at the pump. Additionally, this
service maintains a list of over 3,000
locations that have packaged DEF, and
a majority of the locations are in the
U.S. As truck stops such as Travel
Centers of America roll out on-island
DEF dispensers, they usually
incorporate technology which allows for
single transaction fuel and DEF filling,
which makes buying DEF quicker, more
efficient, and customer-friendly. Onisland DEF dispensing typically requires
truck stops to utilize a mini-bulk system
with at least 800-gallon above ground
storage tanks or even larger
underground storage tanks. The
transition to larger tanks supports bulk
purchases as well as cheaper end-user
prices for DEF. This information is
consistent with the survey information
discussed above.
Regarding DEF quality, ISO 22241–1
sets forth generally accepted industrywide quality specifications for DEF that
were developed by vehicle
manufacturers and other affected
stakeholders. The American Petroleum
Institute (API) Diesel Exhaust Fluid
Certification Program (https://
www.apidef.org) is a DEF quality
licensing program intended to ensure
that DEF of known specifications and
quality is available. We understand that
more than 20 of the largest producers of
DEF are participating in the
Certification Program and that the
associated DEF Aftermarket Audit
Program has also begun. In 2010, API
tested all licensed products and the vast
majority of those products met the ISO
22241–1 specifications. Where
deficiencies were found, API and DEF
manufacturers are working to identify
the cause and helping to ensure that
future batches conform to the ISO
specifications. Because of API’s Audit
Program and its responsiveness to failed
test results, we believe good quality DEF
is broadly and generally available. API’s
Certification and Audit Programs were
developed under the SCR Stakeholder
Group, an informal consortium of
vehicle/engine manufacturers, urea
manufacturers, DEF blenders and
distributors, and associated technology
companies. EPA has been an active
participant in the Stakeholder Group for
several years. We also understand that
the Petroleum Equipment Institute, its
members, and associated stakeholders
have developed Recommended
Practices for the Storage and Dispensing
of Diesel Exhaust Fluid (DEF), which
will provide useful advice to any party
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who stores and dispenses DEF. Given
that the vast majority of DEF production
is accounted for in API’s certification
program and that the follow-up audit
program is showing high rates of
conformance to the ISO specifications,
we believe these programs will be
adequate to ensure DEF quality.
VI. Reasons for Revised Guidance
Considering the developments in
SCR-related technologies, DEF
infrastructure, and the other available
information described above, we believe
it is appropriate to further refine our
guidance to manufacturers regarding
certification of SCR-equipped engines to
be compliant with applicable
regulations. As discussed in this section
of the document, on-highway heavyduty diesel SCR systems introduced into
commerce to date have been highly
successful in inducing operators to refill
DEF tanks on a timely basis and to avoid
interfering with SCR operation, with a
few specific exceptions.18 At the same
time, the Agency believes it is
appropriate to refine its guidance,
particularly as experience is gained with
SCR in-use and as technology advances.
We seek comment on the draft guidance
and interpretations presented here and
plan to incorporate what more we learn
in the next version of the guidance to be
issued later this year.
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A. Current SCR Systems Are Highly
Effective in Use
As trucks equipped with SCR systems
have been introduced into U.S.
commerce, drivers have become familiar
with this technology. Current
information concerning in use operation
of SCR-equipped trucks, including all of
the studies and other information
discussed above, indicates that warning
signals work correctly and that drivers
do not wait for SCR-related
inducements to be triggered to ensure
appropriate and continuing operation of
the systems. Specifically, the
overwhelming majority of drivers
surveyed by CARB, ATA, and Cummins
did not wait for activation of warning
indicators prior to refilling their DEF
tanks and, where warnings did occur,
generally did not drive distances long
enough to lead to activation of
inducements. Further, as the
infrastructure for making DEF available
becomes even more widespread, drivers
will have increased and more
convenient access to DEF when they
need it. As documented in part by
18 It is worth noting again in this context that
under Section 203(a)(3) of the Clean Air Act,
tampering with SCR systems or other emission
controls is prohibited.
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CARB’s survey, there are currently few
availability issues and those appear to
stem primarily from limited situations
where DEF was not found at the first
location at which it was sought. As DEF
infrastructure and supply continue to
expand, EPA also expects the price of
DEF to decrease, in part because of the
move to bulk dispensing that is already
underway. In addition, EPA expects that
the DEF quality assurance programs
described above will make it
increasingly easy for drivers to find DEF
which meets the specifications
necessary for proper operation of the
SCR systems. The strong indication
from all of this evidence is that DEF
warning systems are working correctly,
and that when warned, drivers have not
continued to drive distances long
enough to lead to inducements.
Inducements appear to be triggered in
very few cases.
Navistar’s study and CARB’s field
evaluation provide some evidence
indicating that in some cases there have
been issues related to SCR-equipped
engines and assurance of their proper
operation. Navistar’s study identifies
specific problems associated with the
design or manufacture of certain SCRequipped engines, and outlines the
intentional actions taken by drivers
employed by Navistar’s contractor in
conducting the study. The study’s
findings are properly considered in the
context of all the available information
on SCR operation. In light of the
investigations and surveys conducted by
CARB, ATA, and Cummins, EPA does
not believe Navistar’s findings reflect
the overall efficacy of SCR systems on
heavy-duty diesel engines currently in
operation or the way they are actually
used.
Most of Navistar’s findings resulted
from actions by the contractor’s drivers
to intentionally circumvent the
manufacturer-designed inducements of
the three test vehicles. For example,
drivers avoided triggering inducements
associated with an empty DEF tank by
limiting refueling quantities or keeping
the truck running when it normally
would be turned off. Both ways of
circumventing the inducements exact
their own costs on drivers in terms of
time, convenience, and expense. To
illustrate, never refilling above about
30% of the tank leads to approximately
three times as many refueling events,
and the time and expense associated
with this kind of disruption detract from
the efficient operation of truck
operators, who work in a competitive
business. Navistar’s contract drivers also
disconnected and reconnected various
SCR system components as a means of
avoiding DEF inducements. Such
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intentional actions would be considered
tampering and are illegal.19 While it is
possible that drivers could intentionally
take such actions to circumvent
inducements, manner of truck operation
conducted in the Navistar study is
clearly not representative of the vast
majority of truck operation, as indicated
by the CARB and ATA surveys. We do
not think that the marginal cost and
effort involved in purchasing DEF
provide sufficient motivation for a
driver to follow such inconvenient and
risky courses of action.
We also do not agree with Navistar’s
view that initial inducements are
ineffective to produce corrective
responses by drivers. ATA’s fleet survey
indicates that drivers do not favor
inducements involving an engine power
derate, especially if it occurs while a
truck under heavy load is driving uphill. Thus, drivers are likely to maintain
proper SCR operation to avoid
encountering these inducements.
CARB’s investigation shows that most
inducements functioned properly
during expected truck operating
conditions and their assessment of the
effectiveness of initial inducements was
contrary to Navistar’s findings. CARB
determined that the inducements were
effective because operating in a way that
avoids the inducement strategies and
raise the risk of costly repairs would not
be worth the downtime and potential
financial loss to business. In fact,
Cummins’ survey, which included some
of the same 15-liter engines in Navistar’s
study, found that surveyed trucks
operated with DEF in their tanks for
greater than 99.9 percent of their total
operation. Cummins’ survey also found
that trucks operated with unacceptable
DEF quality for less than 0.18 percent of
their total operation. This strongly
indicates that the inducements have the
intended effect of motivating
appropriate driver behavior.
The report of Navistar’s study found
that some manufacturers’ designs did
not adequately detect water in the urea
tank and thus did not prevent the driver
from refilling the tank with something
other than DEF. Navistar and CARB
findings on DEF quality detection were
not consistent in all cases. For example,
Navistar found that initial and final
inducements for the Freightliner
Cascadia equipped with the 12.8-liter
Detroit Diesel DD13 engine were not
triggered when the DEF tank was filled
with water. During CARB’s field
investigation, both the initial and final
inducements were implemented for Test
19 Such actions are illegal, unless conducted as
part of a testing program covered by an Agencyissued testing exemption.
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Vehicle 1 as expected when the DEF
tank was filled with water. CARB’s
investigation discovered various
production defects for Test Vehicles 2
and 3 that prevented the systems from
working fully (as designed, the systems
appeared to have sufficient capabilities
to detect and respond to DEF quality
problems). CARB followed up with
Cummins and learned that the
manufacturer was aware of the
performance problems and addressing
them in a manner consistent with
regulatory provisions governing defect
reporting and repair.20 The defect
reports submitted by Cummins
corroborated that the manufacturer was
appropriately responding to the
problems. Additionally, Detroit Diesel
informed EPA that they knew of
problems with their system and had
developed an updated software
calibration to fix them as early as June
2010, prior to Navistar reporting the
results of their study. Detroit Diesel has
since begun addressing the problems on
in use trucks consistent with regulatory
provisions governing defect reporting
and repair. As noted above, the
problems with detecting water in the
urea tank appear to be related to defects
in production of these engines, as
opposed to deficient designs. These
production defects are being addressed
in the same manner that problems with
new technology are addressed under
EPA’s regulations.
B. Regulations Should Be Applied in
Light of Continuing Information and
Process Improvements
EPA’s regulatory provisions for
adjustable parameters are intended to
ensure that manufacturers design their
emissions control system in a way that
makes it unlikely that they will be
operated inappropriately. It appears that
manufacturer’s past SCR designs and
EPA’s guidance have resulted in highly
effective controls to protect the
operation of SCR systems, as evidenced
by the surveys and other data which
show that drivers are properly operating
their SCR-equipped trucks. There have
been indications of specific problems
with some engines in-use, and the
manufactures involved have been
addressing them through production
and other improvements as the
problems are identified. We believe it is
appropriate to evaluate the experience
gained to date and to make continuing,
appropriate adjustments to our
certification process for SCR-equipped
engines as technology evolves and inuse experience is gained. EPA
recognizes that development of even
20 See
40 CFR Part 85, Subpart T.
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more robust sensors and inducements
does not negate past approaches
implemented pursuant to existing
regulations. Rather, continual
improvement is expected given the
mounting experience with, and the
maturing of, SCR technology, and the
greater availability of DEF. As improved
strategies and capabilities for proper
SCR operation become feasible, EPA
may guide their application to provide
even further assurance that the
technology is operating as intended on
SCR-equipped engines.
C. As SCR Technology Matures, Further
Guidance Is Appropriate
Several developments in SCR
technology allow continuing refinement
in SCR design. One area of potential
improvement in design involves sensors
that can detect poor quality DEF.
Current SCR system designs incorporate
NOX sensors to determine catalyst
efficiency and detect catalyst
malfunction. Since the sensors are part
of the system design, they have also
been used to detect poor quality DEF
through correlation of NOX emission
rates with various concentrations of
urea. Urea quality sensors have been
identified as a means to help improve
detection capabilities for poor quality
urea. They directly measure quality and
appear likely to represent a quick
detection method for addressing quality
concerns. Manufacturers are currently
evaluating the performance and
durability of various sensor designs.
Since the 2010 model year,
manufacturers have also been refining
their engine/vehicle system diagnostics
software to incorporate additional
capabilities for implementing SCRrelated inducements. For example,
many manufacturers today have
developed multiple triggers for
triggering inducements, including
detection of refueling, extended idling,
and engine shutdown events.
Incorporation of additional inducement
triggers into designs further decreases
the likelihood of improper operation of
the SCR system. Manufacturers are also
improving their diagnostics software to
ensure that SCR-related inducements
cannot be reset or erased by diagnostic
scan tools available to the general public
or by disconnecting components in the
field.
Many manufacturers are
implementing improved designs in their
2011 model year engines/trucks that
may be sold in the State of California.
After the July 2010 public workshop,
CARB and EPA began encouraging
manufacturers to adopt the elements of
design that were discussed. In order to
avoid the need for multiple engine/
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32893
vehicle production designs,
manufacturers have often incorporated
the design elements of vehicles sold in
California into their 49-state vehicles.
Improving sensor capabilities and
inducement strategies should present
low risk and little burden for both
manufacturers and drivers.
Manufacturers are already in the process
of improving their SCR designs, and
overwhelmingly drivers are not waiting
for SCR-related warnings or
inducements to be triggered before they
refill DEF tanks and otherwise maintain
proper operation of SCR systems. Given
the importance of reducing NOX
emissions from heavy-duty diesel
engines for attaining and maintaining
national air quality standards, we have
developed the following draft revised
guidance to reflect improving
capabilities for designing SCR systems
to ensure proper operation.
VII. SCR Adjustable Parameter Design
Criteria
This section discusses design criteria
for on-highway heavy-duty diesel
vehicles or engines using SCR
technology. EPA believes that vehicles
and engines that meet these design
criteria would meet the requirements of
the regulations regarding adjustable
parameters. EPA will still review each
certification application to ensure that
the regulatory provisions are met.
Likewise, in the case of design criteria
that are not fully specified in this
guidance, EPA will review the
application to ensure that the engine
design meets the regulatory
requirements. EPA may review and
revise this guidance as the technology
continues to mature and as EPA receives
more information regarding the use of
SCR systems. In addition, manufacturers
may present other designs for EPA
consideration. All designs will remain
subject to EPA approval under the
existing certification regulations.
As noted above, in determining the
adequacy of an engine’s means of
inhibiting adjustment of a parameter,
EPA considers the likelihood that
settings other than the manufacturer’s
recommended setting will occur in use.
With this in mind, EPA is providing
these draft SCR adjustable parameter
design criteria based on our view that an
SCR-equipped vehicle that complies
with these criteria will be adequately
inhibited from use when the SCR
system is not operating properly.
EPA is asking for comments on the
draft guidance discussed below. The
design criteria are divided into four
categories. The categories are:
A. Reductant tank level driver
warning system.
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B. Reductant tank level driver
inducement.
C. Identification and correction of
incorrect reducing agent.
D. Tamper resistant design.
A. Reductant Tank Level Warning
System
The emissions performance of SCRequipped vehicles depends on having
an adequate supply of appropriate
quality reducing agent in the system.
SCR systems require regular user
interaction to ensure that the system is
operating properly. Therefore, it is
critical that the operator both know
when reducing agent is needed and
have enough time to replace it before it
runs out. A properly designed driver
warning system should address these
concerns.
To achieve this design goal, under our
criteria, the manufacturers would use a
warning system including the following
features:
1. The warning system should
incorporate visual and possibly audible
alarms informing the vehicle operator
that reductant level is low and must
soon be replenished. The manufacturer
should design the warning system to
activate well in advance of the reducing
agent running out so that the operator is
expected to have one or more refueling
opportunities to refill the reductant tank
before it is empty.
2. The warning alarm(s) should
escalate in intensity as the reducing
agent level approaches empty,
culminating in driver notification that is
difficult to ignore, and cannot be turned
off without replenishment of the
reducing agent.
3. To provide adequate notice, the
visual alarm should, at a minimum,
consist of a DEF level indicator, a
unique light, reducing agent indicator
symbol or message indicating low
reducing agent level. The warning light,
symbol or message should be different
from the ‘‘check engine’’ or ‘‘service
engine soon’’ lights used by the On
Board Diagnostic (OBD) system or other
indicators that maintenance is required.
The symbol or message used as the
warning indicator should unmistakably
indicate to the vehicle operator that the
reducing agent level is low. The
reducing agent indicator symbol shown
below has been generally accepted in
the industry and EPA considers it
acceptable as an indicator of low
reducing agent level.
4. The light, indicator symbol or
message should be located on the
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dashboard or in a vehicle message
center. The warning light or message
does not initially have to be
continuously activated, but as the
reducing agent level approaches empty
the illumination of the light or message
would escalate, culminating with the
light being continuously illuminated or
the message continuously broadcast in
the message center. Many current
designs have been found acceptable and
EPA does not anticipate requiring
changes in the foreseeable future.
Unique SCR system warning lights and
message designs that deviate from
previously approved designs or the
design criteria outlined above would
need to be approved by EPA.
Manufacturers may also incorporate
an audible component of the low DEF
warning system. As the reducing agent
level approaches empty the audible
warning system should escalate.
B. Low Reductant Level Inducement
The warning systems discussed above
can play a critical role in achieving
vehicle compliance. As noted, a well
designed warning system should deter
drivers from operating SCR-equipped
vehicles without reducing agent.
However, we believe an additional,
stronger deterrent is necessary and
appropriate. Therefore, at some point
after the operator receives the initial
signal warning that reductant level is
low, it is important that the engine
design incorporates measures to induce
users to replenish the reducing agent.
Under these design criteria,
manufacturers would design their
engines with a final inducement system
that accomplishes the following when
the reductant tank is empty or the SCR
system is incapable of proper dosing:
1. Maximum vehicle speed is
decreased at the quickest safe rate to 5
miles per hour while the vehicle is
operating; or
2. The maximum engine fueling and
engine speed are decreased at the
quickest safe rate while the vehicle is
operating, resulting in engine shutdown
or limiting operation capability to idle
only.
Some manufacturers prefer to trigger
the above final inducement only when
the vehicle has stopped at a safe
location. Under this approach, a vehicle
may be assumed to be in a safe location
if the engine is purposefully shut off
(key turned to the off position), has
experienced an extended idle of 60
minutes (as indicated by zero vehicle
speed for 60 minutes), or a refueling
event has occurred (meaning a volume
of fuel has been added equal to or
greater than 15 percent of vehicle
operating fuel capacity).
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If a manufacturer chooses to
implement final inducement only when
the vehicle is stopped, we believe the
engine will need to be designed with the
following additional characteristics:
a. Be able to trigger final inducement
when the vehicle is stopped at a safe
location. The final inducement will
consist of limiting the vehicle speed to
5 mph, shutting the engine down, or
limiting engine operation to idle only.
b. Prior to triggering final inducement,
be able to impose a severe inducement
which makes prolonged operation of the
vehicle unacceptable to the driver and
compels the driver to replenish the
reducing agent prior to the SCR system
becoming incapable of proper dosing.
The severe inducement will consist of
an engine derate, a vehicle speed
limitation, or a limitation on the number
of engine restarts. For example, an
engine torque derate of 40 percent may
be utilized as a severe inducement for
the operator of a Class 8 line-haul truck
to replenish the reducing agent. The
severe inducement should occur while
there is enough reductant in the tank to
continue to provide proper SCR dosing
for approximately one full day of
vehicle operation. For example, it may
be appropriate to initiate severe
inducement with a 10 percent reserve of
reducing agent in the reductant tank.
c. Be able to determine when the
vehicle has arrived at a safe location for
the purpose of imposing a final
inducement. Such a determination will
be based upon the vehicle experiencing
the next key-off, refueling, or 60-minute
idling event after imposing severe
inducement. During the course of one
day of vehicle operation, EPA believes
it sufficiently likely an operator will
encounter one of the three events
triggering final inducement. In the
unlikely scenario that one of the three
events is not encountered, the severe
inducement should still provide
sufficient incentive for the operator to
refill the reductant tank.
The above final and severe
inducements are not meant to limit the
use of other inducements prior to severe
or final inducement. EPA encourages
the use of additional inducements
which would serve to minimize the
amount of time either severe or final
inducements are encountered.
When developing inducement
strategies for review by EPA at the time
of certification, manufacturers should be
prepared to detail the type and level of
inducements chosen and demonstrate
how they will sufficiently compel
drivers to maintain appropriate
reductant levels and ensure vehicle
operation is limited only to periods
when proper SCR dosing is occurring.
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EPA believes that an engine that is
designed with warning and inducement
strategies consistent with those above
will be highly unlikely to be driven with
an empty reductant tank, and therefore
that such an engine would be
adequately protected from operation
with an empty tank.
C. Identification and Correction of
Incorrect Reducing Agent
Assuring that an SCR-equipped
engine is unlikely to be operated
without proper reducing agent calls for
an SCR system design that is able to
detect incorrect or poor quality reducing
agent. As noted above in the context of
maintaining an adequate level of
reducing agent, the emissions
performance of SCR-equipped vehicles
is dependent on having reducing agent
in the system and the reducing agent
must be of the proper quality. Therefore,
the system must be able to identify and
appropriately respond to poor reductant
quality such as filling the reductant
storage tank with a fluid other than the
manufacturer-specified reducing agent,
or with excessively diluted reducing
agent. An example would be filling the
tank with water rather than DEF, when
DEF is the specified reducing agent.
Current urea-based SCR technology
uses a robust NOX sensor system to
detect poor quality reductant. High NOX
emissions can be correlated to poor
reductant quality and NOX sensors are
already part of the SCR system. Urea
quality sensors directly measure DEF
quality and appear likely to represent a
quick detection method for addressing
quality concerns in the future.
Manufacturers are currently evaluating
the performance and durability of
various sensor designs.
NOX sensor systems will take
somewhat longer to detect poor quality
reducing agent compared to urea quality
sensors. Under ideal conditions, NOX
sensors can detect poor quality in 20
minutes, but may take as long as one
hour to detect poor quality reductant.
An advantage of urea quality sensors is
that, once fully developed, they will
provide operator notification of poor
quality while the vehicle is still at a
filling location.
Because NOX sensors do not directly
measure DEF quality, they do not detect
variations in DEF quality as small as
those detected by urea quality sensors.
However, NOX sensors adequately
detect water which is the most likely
substitute for DEF. Therefore, NOX
sensors are likely able to detect and
prevent the majority of serious quality
problems. Because of the ability of urea
quality sensors to detect smaller
concentration deviations in urea quality,
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we believe urea quality sensors will
soon be the best reasonable technology
to help manufacturers meet the
adjustable parameter requirement. Urea
quality sensors will also permit the
emission control system to adjust DEF
dosing based on the detected quality of
the DEF and, in conjunction with the
inducement strategies, help ensure that
only compliant DEF is used. We expect
urea quality sensors to be available for
use in 2013 model year vehicles.
Under these design criteria, the
engine design would have the following
features to identify and respond
appropriately to poor quality reducing
agent or incorrect fluid:
1. Given the current technology, we
believe manufacturers should be
capable of detecting poor reductant
quality within one hour. As improved
technology becomes available, such as
urea quality sensors, manufactures
should decrease the likelihood, and
increase the performance consequences
of operation with poor quality reductant
by incorporating the technology which
best and most promptly detects poor
reductant quality.
2. Immediately upon detection, the
operator should be notified of the
problem with warnings similar to those
discussed above for inadequate
reductant level. EPA expects the
warning light or message addressing
incorrect reducing agent would quickly
increase in intensity to be continuously
activated.
3. Given the current state of
technology, the engine design should
implement final inducement while the
vehicle is operating and within 4 hours
of detection. Alternately, if a
manufacturer chooses to implement
final inducement when the vehicle is
stopped at a safe location, the engine
design should implement severe
inducement and search for final
inducement triggers within 4 hours of
detection. For this alternate approach,
some lesser inducement should precede
severe inducement at 2 hours after
detection. While we believe it is
appropriate that the vehicle respond in
a similar manner when poor quality
reducing agent is detected as when the
vehicle runs low on reducing agent, we
believe the inducement should not
begin immediately. It is currently
possible for a driver to receive poor
quality reductant unknowingly and for
a driver to need a certain amount of
time after being alerted to the problem
to have it remedied. Therefore, we think
it currently appropriate to allow no
more than 4 hours of operation
following detection before imposing
severe or final inducement. The 4 hours
until severe or final inducement will
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32895
allow the operator sufficient time to
reach a service facility to remedy the
problem.
4. If poor quality reductant is detected
again within 40 hours after putting
proper reducing agent in the tank, then
the operator should be immediately
notified and the poor quality final
inducement or the alternate severe
inducement approach should begin
immediately. We believe continuing to
monitor for repeat instances of poor
quality reductant for 40 hours is likely
to capture the vast majority of operators
intentionally trying to circumvent SCR
controls.
EPA believes design requirements that
alert the operator to inadequate
reducing agent and that institute
inducements to assure correction of
reducing agent quality are needed in
order to ensure that the ‘‘adjustable
parameter’’ of reductant quality is
sufficiently limited. EPA believes that
the warnings and inducements
associated with poor quality reducing
agent discussed above are burdensome
enough that they ensure that
introduction of poor quality reductant
would not occur often or purposely and
that in the unlikely event it occurs,
proper actions will be taken within
reasonable time limits to adequately
minimize the operation of the vehicle/
engine with poor quality reductant and
associated excess emissions. We also
believe the 4 hours until severe or final
inducement is currently needed to allow
the operator to locate and drive to a
service facility capable of draining and
refilling the tank.
EPA believes that an engine that is
designed with the warning and
inducement strategies discussed above
will be highly unlikely to be driven with
inadequate reductant for any significant
period, and therefore that such an
engine would be adequately protected
from operation with inadequate
reductant.
D. Tamper Resistant Design
SCR systems should be designed to be
tamper resistant to reduce the likelihood
that the SCR system will be
circumvented or that the operating
parameters of the system will be
purposefully or inadvertently altered.
Manufacturers should be careful to
review any element of design that
would prevent the proper operation of
the SCR system to make tampering with
that element of design impossible or
highly unlikely. Manufacturers will
have to demonstrate to EPA that their
SCR system design is tamper resistant.
40 CFR 86.094–22(e) contains
provisions regarding actions and criteria
to ensure that elements of design related
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to the adjustable parameters of DEF
level and quality are adequately
inaccessible, sealed, physically limited
or stopped, or otherwise inhibited from
adjustment.
1. At a minimum, the following
actions, if done intentionally, would be
considered tampering and
manufacturers should design their SCR
systems to ensure that restraints on such
actions, whether purposeful or not, are
adequate and such results are unlikely:
a. Disconnected reductant level sensor
b. Blocked reductant line or dosing
valve
c. Disconnected reductant dosing valve
d. Disconnected reductant pump
e. Disconnected SCR wiring harness
f. Disconnected NOX sensor (that is
incorporated with the SCR system)
g. Disconnected reductant quality sensor
h. Disconnected exhaust temperature
sensor
i. Disconnected reductant temperature
sensor
final inducement, or the alternate severe
inducement approach, should begin
immediately. We believe continuing to
monitor for repeat instances of
tampering for 40 hours is likely to
capture the vast majority of operators
intentionally trying to circumvent SCR
controls.
EPA believes that an engine that is
designed with the warning and
inducement strategies discussed above
will be highly unlikely to be driven for
any significant period under the
aforementioned conditions, and that
such an engine would be adequately
protected from operation under such
circumstances.
2. EPA believes that the warnings and
inducements described above for
incorrect reducing agent would also be
adequate under 40 CFR § 86.094–22(e)
to prevent tampering or accidental
actions causing the above results. The
engine should be able to detect
tampering as soon as possible, but no
longer than one hour after a tampering
event.
3. Immediately upon detection, the
operator should be notified of the
problem.
4. We believe the inducement should
not begin immediately. It is possible
that a part failure that occurs in the
course of normal operation will be
recognized as a result of these
diagnostics. An operator should not
immediately receive inducement for an
event which may not have been caused
by tampering. Therefore, we think it
appropriate to allow 4 hours of
operation following detection before
implementing final inducement while
the vehicle is in operation. Alternately,
if a manufacturer chooses to implement
final inducement when the vehicle is
stopped at a safe location, the engine
design should implement severe
inducement and search for final
inducement triggers within 4 hours of
detection. For this alternate approach,
some lesser inducement should precede
severe inducement at 2 hours after
detection. The 4 hours until severe or
final inducement will allow the operator
sufficient time to reach a service facility
to remedy the problem.
5. If tampering of the same component
is detected again within 40 hours after
repair, then the operator should be
immediately notified and the tampering
Dated: May 27, 2011.
Margo Tsirigotis Oge,
Director, Office of Transportation and Air
Quality, Office of Air and Radiation.
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VIII. Conclusion
EPA is releasing this draft document
for comments. We will continue to work
with manufacturers, other stakeholders,
and the public regarding issues related
to its existing regulatory requirements
and SCR technology.
[FR Doc. 2011–13851 Filed 6–6–11; 8:45 am]
BILLING CODE 6560–50–P
these elevations, once finalized, will be
used by insurance agents and others to
calculate appropriate flood insurance
premium rates for new buildings and
the contents in those buildings.
DATES: Comments are to be submitted
on or before September 6, 2011.
ADDRESSES: The corresponding
preliminary Flood Insurance Rate Map
(FIRM) for the proposed BFEs for each
community is available for inspection at
the community’s map repository. The
respective addresses are listed in the
table below.
You may submit comments, identified
by Docket No. FEMA–B–1194, to Luis
Rodriguez, Chief, Engineering
Management Branch, Federal Insurance
and Mitigation Administration, Federal
Emergency Management Agency, 500 C
Street, SW., Washington, DC 20472,
(202) 646–4064, or (e-mail)
luis.rodriguez1@dhs.gov.
Luis
Rodriguez, Chief, Engineering
Management Branch, Federal Insurance
and Mitigation Administration, Federal
Emergency Management Agency, 500 C
Street, SW., Washington, DC 20472,
(202) 646–4064, or (e-mail)
luis.rodriguez1@dhs.gov.
FOR FURTHER INFORMATION CONTACT:
The
Federal Emergency Management Agency
(FEMA) proposes to make
determinations of BFEs and modified
BFEs for each community listed below,
in accordance with section 110 of the
Flood Disaster Protection Act of 1973,
42 U.S.C. 4104, and 44 CFR 67.4(a).
These proposed BFEs and modified
BFEs, together with the floodplain
management criteria required by 44 CFR
60.3, are the minimum that are required.
They should not be construed to mean
that the community must change any
existing ordinances that are more
stringent in their floodplain
management requirements. The
community may at any time enact
stricter requirements of its own or
pursuant to policies established by other
Federal, State, or regional entities.
These proposed elevations are used to
meet the floodplain management
requirements of the NFIP and also are
used to calculate the appropriate flood
insurance premium rates for new
buildings built after these elevations are
made final, and for the contents in those
buildings.
Comments on any aspect of the Flood
Insurance Study and FIRM, other than
the proposed BFEs, will be considered.
A letter acknowledging receipt of any
comments will not be sent.
National Environmental Policy Act.
This proposed rule is categorically
SUPPLEMENTARY INFORMATION:
DEPARTMENT OF HOMELAND
SECURITY
Federal Emergency Management
Agency
44 CFR Part 67
[Docket ID FEMA–2011–0002; Internal
Agency Docket No. FEMA–B–1194]
Proposed Flood Elevation
Determinations
Federal Emergency
Management Agency, DHS.
ACTION: Proposed rule.
AGENCY:
Comments are requested on
the proposed Base (1% annual-chance)
Flood Elevations (BFEs) and proposed
BFE modifications for the communities
listed in the table below. The purpose
of this proposed rule is to seek general
information and comment regarding the
proposed regulatory flood elevations for
the reach described by the downstream
and upstream locations in the table
below. The BFEs and modified BFEs are
a part of the floodplain management
measures that the community is
required either to adopt or to show
evidence of having in effect in order to
qualify or remain qualified for
participation in the National Flood
Insurance Program (NFIP). In addition,
SUMMARY:
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[Federal Register Volume 76, Number 109 (Tuesday, June 7, 2011)]
[Proposed Rules]
[Pages 32886-32896]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-13851]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 86
[FRL-9315-2]
Control of Emissions From New Highway Vehicles and Engines;
Guidance on EPA's Certification Requirements for Heavy-Duty Diesel
Engines Using Selective Catalytic Reduction Technology
AGENCY: Environmental Protection Agency (EPA).
ACTION: Request for comments.
-----------------------------------------------------------------------
SUMMARY: EPA is requesting comment on draft guidance and related
interpretations concerning the application of certain emission
certification regulations to those on-highway heavy-duty diesel engines
that are using selective catalytic reduction systems to meet Federal
emission standards. EPA will review the comments and provide final
guidance and interpretations in a future Federal Register document.
DATES: Any party may submit written comments by July 7, 2011.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2010-0444, by one of the following methods:
On-line at https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: a-and-r-docket@epa.gov.
Fax: (202) 566-1741.
Mail: Air and Radiation Docket, Docket ID No. EPA-HQ-OAR-
2010-0444, Environmental Protection Agency, Mailcode: 6102T, 1200
Pennsylvania Avenue, NW., Washington, DC 20460. Please include a total
of two copies.
Hand Delivery: EPA Docket Center, Public Reading Room, EPA
West Building, Room 3334, 1301 Constitution Avenue, NW., Washington, DC
20460. Such deliveries are only accepted during the Docket's normal
hours of operation, and special arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2010- 0444. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or e-mail. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an e-mail comment directly to EPA without
going through https://www.regulations.gov your e-mail address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of encryption, and be free of
any defects or viruses. For additional information about EPA's public
docket, visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm. For additional instructions on submitting
comments, go to ``What Should I Consider as I Prepare My Comments for
EPA?''
Docket: All documents in the docket are listed in the https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Air and Radiation
Docket, EPA/DC, EPA West, Room 3334, 1301 Constitution Ave., NW.,
Washington, DC. The Public Reading Room is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding legal holidays. The telephone
number for the Public Reading Room is (202) 566-1744, and the telephone
number for the Air Docket is (202) 566-1742.
FOR FURTHER INFORMATION CONTACT: Greg Orehowsky, Heavy-Duty and Nonroad
Engine Group, Compliance and Innovative Strategies Division, Office of
Transportation and Air Quality, U.S. Environmental Protection Agency;
1200 Pennsylvania Avenue, (6405J), NW., Washington, DC 20460. Telephone
number: 202-343-9292; Fax number: 202-343-2804; E-mail address:
Orehowsky.Gregory@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Purpose
This Federal Register document describes and seeks public comment
on draft guidance for complying with adjustable parameter regulations
at 40 CFR 86.094-22 as they apply to certification of on-highway heavy-
duty diesel engines using selective catalytic reduction (SCR)
technology to meet emission standards for oxides of nitrogen
(NOX). This draft guidance includes EPA's interpretation of
relevant regulatory provisions in light of available information on
current and developing approaches for effective SCR controls. After
considering any public comments received, EPA will issue the guidance
and interpretations in the Federal Register, and will use them in
reviewing any application for certification application involving SCR
received on or after the effective date of the guidance. The draft
guidance contained in this document reflects the fact that
manufacturers of heavy-duty engines and operators of trucks have gained
significant experience in the design and use of SCR systems for these
engines, and this experience should be reflected in the certification
process. We invite public comment on the draft guidance and
interpretations set forth below.
Until the effective date of the final guidance and interpretations,
manufacturers should continue to refer to the regulations and the
existing guidance documents noted below and to work with their
certification representatives. We recognize that SCR technology will
continue to mature, and we anticipate that appropriate designs
[[Page 32887]]
for heavy-duty diesel vehicles and heavy-duty diesel engines using SCR
systems may continue to evolve as additional experience with the
technology is gained.
This draft document provides specific examples of how we interpret
existing certification regulations and how we intend to apply these
regulations to heavy-duty diesel engines using SCR systems, based on
the information available to us. These examples are not exclusive and
are to be considered examples. Manufacturers remain able to present
their own unique strategies that are not the same as the examples we
are providing, and such strategies will remain subject to our review
and approval under the certification regulations. Manufacturers must
still show EPA that they meet all statutory and regulatory requirements
when they apply for certification.
II. Overview
In promulgating the 0.20 gram per brake horsepower-hour
NOX standard for 2010 model year heavy-duty diesel engines,
based on a specified regulatory test procedure, EPA recognized SCR
technology as one potential approach for achieving the required
emission reductions. EPA identified several issues for manufacturers to
address in developing and applying SCR technology. Those issues related
largely to the technology's use of a chemical reducing agent to reduce
NOX emissions. The reductant is generally in liquid form,
which is referred to in this document as DEF (``diesel exhaust
fluid''). DEF is stored in a tank located on the vehicle and is
injected into the exhaust downstream of the engine. SCR technologies
require drivers to refill DEF on a regular basis and are dependent on
appropriately broad availability of DEF.\1\ EPA regulations governing
certification of engines generally require manufacturers to show that
emission control technologies are adequately designed to limit
adjustments that may increase emissions (``adjustable parameters,''
discussed in detail below). SCR is unique among emission controls in
that it requires on-going driver interaction to ensure proper operation
of the system.
---------------------------------------------------------------------------
\1\ A Class 8 truck equipped with standard dual 150-gallon fuel
tanks can travel approximately 3,600 miles between DEF tank refills,
assuming a 20-gallon DEF tank and representative DEF dosing rate of
3 percent of fuel usage. DEF price varies depending on whether it is
supplied via bulk container (commonly used by fleets and growing
numbers of truck stops) or a 1 to 2.5-gallon jug. Current prices for
bulk DEF at a truck stop are generally less than $3.00 per gallon
and jug prices can be $4.00 or more per gallon.
---------------------------------------------------------------------------
To comply with the NOX standard, most heavy-duty engine
manufacturers developed SCR systems because of their high efficiency in
reducing NOX emissions. A relatively unsophisticated SCR
system can achieve 60 percent reduction and a robust system can achieve
greater than 80 percent reduction. This enables engine calibrations
that increase fuel economy. Additionally, SCR technology has a
relatively lower cost compared to NOX adsorber technology.
In developing SCR systems, manufacturers consulted with EPA about
how SCR systems could be designed and what other steps would be needed
(e.g., concerning DEF availability) to allow SCR to be used consistent
with EPA regulations. Over a period of years, EPA has developed and
refined guidance to address how manufacturers could effectively address
issues related to compliance with the regulations for adjustable
parameters. Manufacturers have addressed the adjustable parameter
regulations by designing engines that employ warning systems for the
driver and engine operation-related inducements for drivers to refill
DEF tanks with proper DEF.
Manufacturers have also worked to increase DEF availability through
infrastructure development. DEF infrastructure and sales volume have
continued to grow since introduction of 2010 model year trucks equipped
with SCR systems. Initially, DEF availability was concentrated around
major truck routes, but has since increased in areas away from these
locations. DEF is now available for sale in every state at truck stops
and service facilities, and is available for delivery to fleet
locations, as well. To assist drivers in finding DEF, multiple
Internet-based DEF locator services have also been developed. Sales
volumes of DEF are increasing significantly and are believed to
correlate with the increased delivery and use of SCR equipped trucks.
Increasing demand supported by sales volume should continue to drive
the expanding infrastructure.
III. Relevant Regulatory Provisions
Under Section 203(a)(1) of the Clean Air Act, engines and/or
vehicles must be certified as conforming with all applicable
regulations before they may be introduced into commerce. Of particular
relevance for on-highway heavy-duty diesel engines using SCR technology
are the provisions that govern adjustable parameters at 40 CFR 86.094-
22.\2\ In particular, 40 CFR 86.094-22(e) authorizes EPA to determine
those vehicle or engine parameters that will be subject to adjustment
for emission testing purposes, and 40 CFR 86.094-22(e)(1) discusses how
the Agency determines which parameters are subject to adjustment.
---------------------------------------------------------------------------
\2\ The regulatory provisions governing allowable maintenance at
40 CFR 86.004-25 and 40 CFR 86.094-25, and auxiliary emission
control devices, or AECDs at 40 CFR 86.004-2, 40 CFR 86.082-2 and 40
CFR 86.004-16 are also relevant to certification of engines using
SCR technology, but are outside the scope of this document.
Manufacturers should continue to refer to existing guidance noted
below covering these regulatory provisions.
---------------------------------------------------------------------------
It is important for manufacturers to control the emissions
performance of an engine or vehicle over the full range of any
adjustable parameter in order to ensure that in-use operation is as
good as projected at the time of certification. When emission-related
parameters can be adjusted, there is a concern that the engine or
vehicle can be operated at settings other than the manufacturer's
recommended setting, possibly increasing emission levels.
If a parameter is subject to adjustment, the engine may be tested
over any point in the range of adjustment and must meet the emissions
standard through the range of adjustment. The Administrator determines
the range of adjustment for emissions testing based on whether the
means used to inhibit improper adjustment (e.g., limits, stops, seals)
are adequate. 40 CFR 86.094-22(e)(2) sets forth how EPA determines the
adequacy of the limits, stops, seals or other means used to inhibit
improper adjustment. For any parameter that is not adequately limited,
40 CFR 86.094-22(e) authorizes EPA to adjust the setting within the
physical limits or stops during certification and other compliance
testing. If a parameter is determined to be adequately inaccessible,
sealed, or otherwise inhibited from adjustment, the vehicle will only
be emission tested at the actual settings to which the parameter is
adjusted during production. 40 CFR 86.094-22(e)(2)(i) and (ii)
identifies certain types of parameters subject to adjustment, and
identifies criteria related to technology, time, or expense for
determining whether adjustment of the parameter is adequately limited.
These provisions indicate that the technology used to limit adjustment,
or the burden on the operator to make an adjustment (e.g., more than
one-half hour in time or more
[[Page 32888]]
than $20.00 in cost),\3\ can be adequate to determine that the
parameter is adequately limited and would not be treated as adjustable
outside of the specified range for purposes of emissions testing for
compliance with the standard. 40 CFR 86.094-22(e)(2)(iv) states that in
determining the adequacy of a physical limit, stop, seal, or other
means used to inhibit adjustment of an adjustable parameter, EPA will
consider the likelihood that settings other than the manufacturer's
recommended setting will occur during in-use operation of the vehicle
or engine, considering such factors as, but not limited to: (1) The
difficulty and cost of getting access to make an adjustment, (2) the
damage to the engine/vehicle if an attempt is made, (3) the effect of
settings beyond the limits, stops, seals, or other means on engine
performance characteristics other than emission characteristics, and
(4) surveillance information from similar in-use vehicles or engines.
---------------------------------------------------------------------------
\3\ This cost is represented in terms of 1978 dollars. Adjusting
for inflation, this would equate to roughly $70.00 in 2011 dollars.
---------------------------------------------------------------------------
The emission control efficiency of an SCR system is highly
dependent on the presence and quality of the reducing agent.
Consequently, it is critical that a SCR-equipped vehicle be designed so
that it is highly unlikely that the vehicle will be used without proper
reducing agent. Given that most SCR system designs store the required
DEF in a tank located on the vehicle and depend on the vehicle operator
to refill the tank with DEF, EPA has indicated in previous guidance
that manufacturers relying on SCR systems for emission control must
incorporate engine design elements that make it highly unlikely the
vehicle will operate for any substantial period without the appropriate
DEF. In practice, this has meant designing engines or vehicles to alert
operators of when the engine will run out of DEF, when the DEF is
inadequate, or if the SCR system is not properly operating due to
tampering or some malfunction. This has also meant designing engines or
vehicles with features that motivate operators to ensure proper use of
the SCR system, such as engine derates and vehicle speed inhibitors.
Engine derates and vehicle speed inhibitors alter important vehicle
performance characteristics, such as acceleration, maximum vehicle
speed attainable, and ability to maintain speed under various loads,
that are clearly noticeable to a driver.
IV. Prior Guidance
On March 27, 2007, EPA issued guidance regarding the certification
of light-duty and heavy-duty motor vehicles and heavy-duty motor
vehicle engines using SCR systems (CISD-07-07).\4\ The purpose of the
guidance was to discuss EPA's intended approach to certification of
engines using SCR technologies and to facilitate manufacturer planning
in advance of certification. EPA noted that several regulatory
requirements are uniquely relevant to the certification and
implementation of engines using SCR, specifically the regulatory
provisions dealing with allowable maintenance and adjustable
parameters. EPA suggested that an SCR system that requires the vehicle
operator to replenish DEF periodically is potentially an adjustable
parameter, and that unless operation of the vehicle without DEF was
sufficiently inhibited through built-in performance deterioration or
some similar system, vehicles using SCR could be treated as having an
adjustable parameter range including no DEF in the tank and could not
be certified if the vehicle would exceed emission standards without DEF
in the tank. EPA provided guidance regarding how engines using SCR
could be designed consistent with these regulatory provisions to allow
for certification of such engines. EPA provided examples of possible
sufficient inducements, including prohibiting operation if DEF is not
present and having vehicle performance degraded in a manner that would
be safe but onerous enough to discourage the user from operating the
vehicle until the DEF tank was refilled. EPA also highlighted the need
to assure that DEF would be available and accessible to operators and
suggested places where DEF could be made available, such as dealerships
and truck stops. We recognized that SCR technology was evolving and
that our guidance also might need to evolve.
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\4\ U.S. Environmental Protection Agency, Dear Manufacturer
Letter regarding ``Certification Procedure for Light-Duty and Heavy-
Duty Diesel Vehicles and Heavy-Duty Diesel Engines Using Selective
Catalytic Reduction (SCR) Technologies,'' March 27, 2007, reference
number CISD-07-07 (LDV/LDT/MDT/HDV/HDE), available at https://iaspub.epa.gov/otaqpub/display_file.jsp?docid=16677&flag=1.
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On February 18, 2009, EPA issued additional guidance (CISD-09-04)
to supplement CISD-07-07.\5\ This guidance provided additional details
regarding certification of heavy-duty engines with SCR systems.
Particularly, it outlined design elements that would make it highly
likely operators would replenish DEF prior to the tank being empty and
operators would not tamper with SCR systems. The guidance provided
specific examples of robust driver warnings and inducements to help
ensure operators addressed conditions such as low reductant level,
improper reductant quality, and tampered system components. EPA
continued to note the potential need for additional guidance or changes
in our approach for SCR certification.
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\5\ See docket number EPA-HQ-OAR-2010-0444-0018.
---------------------------------------------------------------------------
On December 30, 2009, EPA revised CISD-09-04.\6\ The intent of this
revision was to clarify that CISD-09-04 was guidance and did not set
forth binding requirements. EPA revised the guidance and made clear
that manufacturers wishing to certify engines using SCR technology
should consult the revised guidance document as well as the guidance
provided in CISD-07-07. EPA also reminded manufacturers that they
should work with their certification representatives to provide EPA
adequate descriptions of the strategies that are incorporated in their
SCR systems in order to demonstrate compliance with EPA's certification
requirements as set forth in 40 CFR Part 86.
---------------------------------------------------------------------------
\6\ U.S. Environmental Protection Agency, Dear Manufacturer
Letter regarding ``Revised Guidance for Certification of Heavy-Duty
Diesel Engines Using Selective Catalyst Reduction (SCR)
Technologies,'' December 30, 2009, reference number CISD-09-04
(HDDE), available at https://iaspub.epa.gov/otaqpub/display_file.jsp?docid=20532&flag=1.
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EPA has continued to monitor the development of SCR technology and
its effectiveness in achieving emission control in use. On July 20,
2010, in conjunction with the California Air Resources Board (CARB), we
conducted a public workshop to review existing guidance and policies
regarding design and operation of SCR-equipped heavy-duty diesel
engines.\7\ In particular, EPA reviewed approaches to designing SCR-
equipped engines to monitor and induce appropriate responses to
insufficient or improper DEF, as well as strategies regarding SCR
systems that are tampered with or defective. EPA developed a strawman
proposal regarding future certification of heavy-duty diesel engines
equipped with SCR technology,\8\ and opened a docket to allow public
comment regarding these issues.\9\ As part of the strawman, EPA
included approaches for engines
[[Page 32889]]
equipped with SCR, including designs that monitor on-board DEF supply
and induce action to avoid low DEF supply and operation with no DEF (or
an insufficient amount to allow proper dosing). EPA also discussed
detection of poor quality DEF, as well as warnings and inducements if
poor quality DEF is detected. In addition, EPA discussed designs for
engines equipped with SCR systems to sufficiently reduce the likelihood
that SCR system operation would be circumvented. EPA cautioned
manufacturers to review any element of design that could be tampered
with and prevent proper operation of the SCR system. Lastly, EPA noted
DEF freeze protection and infrastructure requirements, and requirements
regarding unregulated pollutants.
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\7\ See 75 FR 39251 (July 8, 2010).
\8\ See docket number EPA-HQ-OAR-2010-0444-0016. The strawman
proposal was not final guidance.
\9\ See 75 FR 39251 (July 8, 2010). Public comments received in
response to the public workshop are available in EPA's docket EPA-
HQ-OAR-2010-0444, available at https://www.regulations.gov.
---------------------------------------------------------------------------
V. Experience to Date
A. EPA's Certification Program
For the 2010 and 2011 model years, EPA has certified a total of 71
on-highway heavy-duty diesel engine families with SCR systems produced
by 11 engine manufacturers. As part of the certification process,
engine manufacturers are required to disclose various aspects of the
SCR system designs, including elements of their system that may be
adjustable parameters. To date, manufacturers' designs have employed
driver warnings and inducements for low reductant level, poor reductant
quality, and tampered or malfunctioning SCR systems.
In order to ensure adequate availability of DEF for use with
manufacturers' engines, at the time of certification EPA reviews
manufacturers' plans for DEF availability and accessibility. EPA
expects manufacturers to have DEF available at their dealerships, to
encourage DEF availability at third-party locations, and to have an
emergency backup plan in case DEF is not readily available.
When manufacturers implement new emission controls, the engine
technology generally evolves and the manufacturers make improvements
over the course of initial model years as they develop and certify
engines and vehicles for each new model year. The process of
certification involves interaction between manufacturers and EPA
technical staff about the nature and effectiveness of emission controls
and often results in manufacturers modifying emission control
strategies based on feedback from EPA. In the case of SCR technology,
manufacturers have certified only a few model years of engines that
incorporate SCR technology, and EPA has seen maturing approaches to
implementing the technology. For example, from the 2010 to 2011 model
years manufacturers improved or developed new engine/vehicle diagnostic
software that provides more or better driver warnings and inducements
related to the SCR system. Similarly, manufacturers are also evaluating
various sensors that are expected to reduce the amount of time
necessary to detect poor quality DEF in future model years. As with
other new engine technologies, defects in the operation of SCR system
strategies (e.g., driver inducements) are sometimes discovered in the
field, and manufacturers initiate campaigns to fix the issues and
incorporate these fixes in current and new model year production
engines.
B. California Air Resources Board SCR Field Evaluation
The California Air Resources Board (CARB) recently conducted field
investigations within the State of California to evaluate
implementation of SCR technology for 2010 model year vehicles.\10\ The
investigations included: (1) A survey of DEF availability, (2) a survey
to determine whether drivers are using DEF or have tampered with SCR
components, (3) an evaluation of SCR driver inducements, and (4) an
evaluation of the potential emissions impact of improper SCR operation.
---------------------------------------------------------------------------
\10\ California Air Resources Board, Report regarding ``Heavy-
Duty Vehicle Selective Catalytic Reduction Technology Field
Evaluation,'' May 2011, available at https://www.arb.ca.gov/msprog/cihd/cihd.htm.
---------------------------------------------------------------------------
CARB conducted surveys of DEF availability in March 2010 and August
2010. Both surveys indicated that DEF is readily available at major
diesel truck stop refueling stations along major interstate highways in
California. In the first survey DEF was determined to be available at
85 percent of refueling stations, and in the second survey DEF was
determined to be available at 92 percent of refueling stations. In
addition, both surveys indicated that 30 percent of retailers that
normally supply parts for heavy-duty vehicles have DEF available. CARB
noted that as older engines are retired and an increasing number of
SCR-equipped engines enter into operation, the availability of DEF
should increase with demand. It concluded that DEF is currently being
offered in adequate supply for the relatively limited number of
vehicles using SCR.
In September 2010, CARB conducted random inspections of 69 trucks
equipped with 2010 model year engines to determine whether DEF was
being used, whether the DEF was of appropriate quality, and whether
driver warning indicators (i.e., warning lights, messages, or audible
alarms) were present. CARB found that all trucks were using DEF and
that the DEF was of appropriate quality. No DEF-related warning
indicators were active and there was no evidence of tampering with SCR
system components. Additionally, CARB solicited information from
drivers about their experience with locating DEF. Sixty drivers
indicated that they encountered no problem locating DEF, while nine
indicated they had minor problems locating DEF in California or in
other states. For those encountering problems, the issue was limited to
not being able to purchase DEF at a particular refueling station and
instead having to purchase it at a different refueling station. Sixty-
eight drivers stated that they never ran out of DEF while operating
their vehicles and only one driver indicated that he drove for only 10
miles with an empty DEF tank as indicated by the driver's gauge.
In the second half of 2010, CARB conducted an evaluation of SCR
inducements on three trucks equipped with 2010 model year engines and
SCR systems. The trucks evaluated were a Freightliner Cascadia equipped
with a 12.8-liter Detroit Diesel DD13 engine (Test Vehicle 1), a
Kenworth T800 equipped with a 14.9-liter Cummins ISX engine (Test
Vehicle 2), and a Dodge 5500 equipped with a 6.7-liter Cummins ISB
engine (Test Vehicle 3). Each truck was operated under various test
conditions to observe the operation of driver inducements and their
effectiveness in compelling the driver to take a particular course of
action. The conditions under which the trucks were operated included:
(1) Operation until the DEF tank was depleted, (2) operation with water
in the reductant tank instead of DEF, and (3) operation with a disabled
DEF system. CARB staff referenced the vehicle owner's manuals and the
February 2009 EPA guidance to ascertain the expected driver warning
indicators and inducement strategies that were expected in each
condition.
On Test Vehicle 1, the warnings and inducements were implemented as
expected. CARB deemed the warnings effective in drawing the driver's
attention to the need for SCR-related service. The initial inducement
incorporated in Test Vehicle 1 was a 25 percent engine torque derate
and a 55 mph speed limitation. CARB concluded that driving the truck
with these inducements was neither acceptable nor tolerable, especially
when trying to accelerate or driving up-hill, and would
[[Page 32890]]
likely cause a driver to refill with DEF or correct the SCR problem as
needed. If the initial inducement were ignored, the severe inducement
incorporated in Test Vehicle 1 was a 5 mph speed limitation, which
worked as designed. The only way to resume normal operation after the
severe inducement was to have the vehicle serviced by draining the
water out of the system, filling the reductant tank with DEF, and
having the system reset by an authorized service technician. CARB
determined that the inducements were effective for this vehicle because
the constant inducement strategies and risk of costly repairs would not
be worth the downtime and financial loss to the business when DEF could
simply have been added to ensure proper vehicle operation.
On Test Vehicles 2 and 3, the warnings and some inducements were
implemented as expected, but certain inducements were not. Test Vehicle
2 implemented the initial inducement (25 percent engine torque derate)
in response to DEF depletion, DEF contamination, and DEF tampering
conditions, but failed to implement the severe inducement (5 mph speed
limitation) in response to any of these conditions. Test Vehicle 3
incorporates an engine no-restart severe inducement after a 500-mile to
no-restart countdown. After the 500-mile countdown reaches zero and a
safe harbor event (key-off) is experienced, the truck should not
restart. The inducement worked as expected in response to DEF
contamination and DEF tampering conditions. In response to the DEF
depletion condition, Test Vehicle 3 started the 500-mile to no-restart
countdown as expected. However, after the countdown reached zero and
the truck was shut off, the truck successfully started the next day and
reset the countdown. On a subsequent restart attempt after the
countdown reached zero, the truck successfully implemented the no-
restart condition.
CARB contacted Cummins, the engine manufacturer for Test Vehicles 2
and 3, about the failures. Cummins was aware of and addressing the
issues underlying the failures. In the case of Test Vehicle 2, Cummins
in the second quarter of 2010 had implemented a correction on their
engine production line and in the third quarter of 2010 had begun a
voluntary recall of the engine family to correct the problem.\11\
Similarly, in the case of Test Vehicle 3, Cummins was aware of a DEF
heater malfunction that contributed to the final inducement not
initiating as expected and was already addressing the issue. CARB
concluded that for both Test Vehicles 2 and 3, the warnings were deemed
effective in drawing the driver's attention to the need for SCR-related
service. CARB also concluded that the inducements on Test Vehicle 2
were difficult to objectively assess due to a malfunctioning throttle
position sensor that was encountered during the testing. CARB concluded
that the inducements on Test Vehicle 3 were effective once the DEF
heater malfunction was corrected.
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\11\ Voluntary recalls are a typical method for manufacturers to
remedy emission-related problems they discover. Manufacturers are
required to report voluntary emission recalls to EPA and ARB, and
Cummins did so in this case.
---------------------------------------------------------------------------
C. American Trucking Associations Survey
In 2010, the American Trucking Associations (ATA) through its
technical advisory group conducted a survey of 12 trucking fleets
operating across the United States regarding their experience operating
trucks with SCR-equipped engines.\12\ The surveyed fleets are some of
the largest in the country and operate an approximate total of 2,000
SCR-equipped trucks. The fleet owners indicated that they would
probably purchase approximately 5,900 SCR-equipped trucks in 2011.
---------------------------------------------------------------------------
\12\ See docket number EPA-HQ-OAR-2010-0444-0019.
---------------------------------------------------------------------------
None of the surveyed fleets reported any problems locating DEF and
none reported an engine derate, vehicle speed limitation, or no-restart
event caused by operation with an empty DEF tank. Similarly, no fleet
reported issues with the quality of DEF. There were six reported
instances of an engine derate resulting from circumstances other than
an empty DEF tank. Two of these instances were caused by malfunctioning
sensors and four were caused by melted DEF supply hoses. None of these
instances were associated with the behavior of the operator. Survey
respondents also reported a total of five instances of NOX
sensor malfunctions, none of which were related to driver
tampering.\13\ ATA's fleet survey indicates that drivers do not favor
inducements involving an engine power derate, especially if it occurs
while a truck under heavy load is driving up-hill.
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\13\ When a manufacturer determines that an emission-related
defect exists in 25 or more engines of the same class or category
and model year, they are required to file an Emission Defect
Information Report in accordance with 40 CFR 85.1901 et seq.
---------------------------------------------------------------------------
D. Cummins Survey
In 2010, Cummins collected information from 47 different customer-
owned vehicles that were equipped with Cummins 11.9-liter and 15-liter
engines using SCR.\14\ The vehicles were equipped with data-loggers
that wirelessly transmit data to Cummins periodically on the operation
of those vehicles. At the time the data was gathered, the vehicles had
accumulated a total of more than 2.4 million miles of operation across
the United States. For approximately 99.7 percent of the operating
miles of the surveyed vehicles, the DEF level was above 10 percent of
tank capacity. For the remainder of vehicle operation:
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\14\ See docket number EPA-HQ-OAR-2010-0444-0020.
---------------------------------------------------------------------------
DEF level was between 5 and 10 percent of tank capacity
for less than 0.13 percent of the operating miles (i.e., approximately
3,000 miles).
DEF level was between 2.5 and 5 percent of tank capacity
for less than 0.03 percent of the operating miles (i.e., approximately
740 miles).
DEF level was between zero and 2.5 percent of tank
capacity (a condition at which engines experienced derated performance)
for less than 0.04 percent of the operating miles (i.e., approximately
920 miles).
DEF level was at zero percent of tank capacity (a
condition at which engines experienced derated performance) for less
than 0.02 percent of the operating miles (i.e., approximately 520
miles).
In addition, DEF quality was unacceptable (i.e., a faulted
condition existed) for less than 0.18 percent of the operating miles
(i.e., approximately 4,400 miles).
E. Navistar EnSIGHT Report
In 2010, Navistar retained EnSIGHT, Inc. to test three 2010 model
year SCR-equipped trucks to analyze inducements provided for in EPA
certification guidance.\15\ The following three trucks were tested: (1)
One Freightliner Cascadia with a 15-liter Detroit Diesel engine, (2)
one Kenworth T-660 with a 15-liter Cummins ISX 15 435B engine, and (3)
one Dodge Ram 5500 crew cab flatbed with a 6.7-liter Cummins ISB 6.7
305 engine. As part of testing, the three trucks were operated with the
intent of circumventing the manufacturer-designed inducements, which is
in contravention to EPA tampering regulations.\16\
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\15\ See docket number EPA-HQ-OAR-2010-0444-0015 for the August
2010 report. Navistar provided EPA with supplemental details on the
August 2010 report in a follow-up October 2010 report. See docket
number EPA-HQ-OAR-2010-0444-0022 for the October 2010 report.
\16\ Section 203(a)(3) prohibits tampering with emission
controls. Such actions are illegal, unless conducted as part of a
testing program covered by an Agency-issued testing exemption.
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[[Page 32891]]
Based on their testing program, EnSIGHT reported the following:
All trucks physically could be operated for extended
periods under an initial inducement. Provided the driver took
particular actions, final inducements could be avoided indefinitely.
For example, the Freightliner Cascadia was driven over 1,000 miles on
an empty DEF tank at a limited speed of 55 mph, which is the initial
inducement. As long as no more than 30 percent of the fuel tank
capacity (approximately 100 gallons) was added at any single refueling
event, the final inducement, a 5 mph vehicle speed limitation was not
triggered. The Kenworth T-660 was driven with an empty DEF tank and a
25 percent engine torque derate, which is the initial inducement. As
long as the engine was not shut off for more than a few minutes at a
time, the 5 mph vehicle speed limitation final inducement was not
triggered.
When DEF tanks were empty and water was added instead of
DEF, two trucks were able to run indefinitely. When the Dodge 5500 was
low on DEF and began its 500-mile to final inducement (i.e., no-restart
condition) countdown, the driver was able to fill the DEF tank with
water, start the truck, and drive normally. This action cleared the
500-mile countdown and the driver display indicated a full DEF tank. On
one test run, the truck displayed visual and audible warning signals
after 73 miles of driving with water in the DEF tank and eventually
displayed the 500-mile to no-restart countdown after 694 miles of
driving. Upon shutting off the truck after a total of 1,278 miles of
driving, a no-restart condition was encountered. On a subsequent test
run with water in the DEF tank, the truck was driven over 4,000 miles
and encountered no warning signals or inducements. The Freightliner
Cascadia was driven over 15,000 miles with only water in its DEF tank
and triggered no initial or final inducement.
SCR system components could be repeatedly disconnected and
reconnected to avoid particular inducements. On the Dodge 5500, the
driver was able to disconnect the injector electrical connector, which
would initiate a 500-mile to final inducement (i.e., no-restart
condition) countdown. As the mileage countdown continued, the driver
could reconnect the component and reset the 500-mile countdown. On the
Freightliner Cascadia, when electrical connections to the DEF injector,
gauge, or tank pump were unplugged, the truck was driven for over 1,000
miles prior to triggering an inducement.
Although the testing program was designed to intentionally
operate the trucks until final inducements were encountered, EnSIGHT
also provided an assessment of the impact of initial inducements on
driver behavior. They concluded that a 25 percent engine torque derate
would not induce a corrective response by the drivers, including when
the truck was fully loaded. With this level of derate, EnSIGHT's
drivers were able to operate the Freightliner Cascadia and the Kenworth
T-660 at speeds up to 55 mph and 65 mph, respectively. Of the Kenworth
T-660, EnSIGHT's drivers indicated that the truck could easily be
operated and was acceptable for typical driving for long periods of
time under derate.
F. DEF Infrastructure and DEF Quality
The DEF infrastructure and sales volume have continued to grow
since introduction of 2010 model year trucks equipped with SCR systems.
Initially, DEF availability was concentrated around major truck stops
and truck routes and 2.5-gallon jugs represented the common mode of
supply. Although very limited, bulk DEF dispensing typically utilized
small storage tanks located apart from the fuel islands at truck stops.
The refilling of fuel and DEF tanks at truck stops was also more likely
to require two separate purchase transactions.
The continually increasing DEF infrastructure and sales volume have
resulted in improved DEF availability along major truck routes as well
as other locations. ``AdBlue and DEF Monitor,'' a publication of
Integer Research, reports that DEF is available for sale in jug form in
every state.\17\ Integer Research also reports that DEF is available
for delivery to fleet locations in every state, as well. To assist
drivers in finding DEF, multiple Internet-based DEF locator services
have been developed. One of these services, DiscoverDEF.com, run by
Integer Research, recently announced that DEF consumption in the U.S.
reached 2.3 million gallons per month in December 2010 and that in
August of the same year consumption volumes increased 43% compared to
the previous month. Also, a number of suppliers reported sales volumes
doubling in September 2010 alone. These increases in DEF consumption
are believed to correlate with the increased delivery and use of SCR-
equipped trucks.
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\17\ See docket number EPA-HQ-OAR-2010-0444-0021.
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Increasing demand supported by sales volume helps drive the
continuing expansion of DEF infrastructure. The same locator service
recently reported that more than 100 truck stops in the U.S. and Canada
now have DEF available at the pump. Additionally, this service
maintains a list of over 3,000 locations that have packaged DEF, and a
majority of the locations are in the U.S. As truck stops such as Travel
Centers of America roll out on-island DEF dispensers, they usually
incorporate technology which allows for single transaction fuel and DEF
filling, which makes buying DEF quicker, more efficient, and customer-
friendly. On-island DEF dispensing typically requires truck stops to
utilize a mini-bulk system with at least 800-gallon above ground
storage tanks or even larger underground storage tanks. The transition
to larger tanks supports bulk purchases as well as cheaper end-user
prices for DEF. This information is consistent with the survey
information discussed above.
Regarding DEF quality, ISO 22241-1 sets forth generally accepted
industry-wide quality specifications for DEF that were developed by
vehicle manufacturers and other affected stakeholders. The American
Petroleum Institute (API) Diesel Exhaust Fluid Certification Program
(https://www.apidef.org) is a DEF quality licensing program intended to
ensure that DEF of known specifications and quality is available. We
understand that more than 20 of the largest producers of DEF are
participating in the Certification Program and that the associated DEF
Aftermarket Audit Program has also begun. In 2010, API tested all
licensed products and the vast majority of those products met the ISO
22241-1 specifications. Where deficiencies were found, API and DEF
manufacturers are working to identify the cause and helping to ensure
that future batches conform to the ISO specifications. Because of API's
Audit Program and its responsiveness to failed test results, we believe
good quality DEF is broadly and generally available. API's
Certification and Audit Programs were developed under the SCR
Stakeholder Group, an informal consortium of vehicle/engine
manufacturers, urea manufacturers, DEF blenders and distributors, and
associated technology companies. EPA has been an active participant in
the Stakeholder Group for several years. We also understand that the
Petroleum Equipment Institute, its members, and associated stakeholders
have developed Recommended Practices for the Storage and Dispensing of
Diesel Exhaust Fluid (DEF), which will provide useful advice to any
party
[[Page 32892]]
who stores and dispenses DEF. Given that the vast majority of DEF
production is accounted for in API's certification program and that the
follow-up audit program is showing high rates of conformance to the ISO
specifications, we believe these programs will be adequate to ensure
DEF quality.
VI. Reasons for Revised Guidance
Considering the developments in SCR-related technologies, DEF
infrastructure, and the other available information described above, we
believe it is appropriate to further refine our guidance to
manufacturers regarding certification of SCR-equipped engines to be
compliant with applicable regulations. As discussed in this section of
the document, on-highway heavy-duty diesel SCR systems introduced into
commerce to date have been highly successful in inducing operators to
refill DEF tanks on a timely basis and to avoid interfering with SCR
operation, with a few specific exceptions.\18\ At the same time, the
Agency believes it is appropriate to refine its guidance, particularly
as experience is gained with SCR in-use and as technology advances. We
seek comment on the draft guidance and interpretations presented here
and plan to incorporate what more we learn in the next version of the
guidance to be issued later this year.
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\18\ It is worth noting again in this context that under Section
203(a)(3) of the Clean Air Act, tampering with SCR systems or other
emission controls is prohibited.
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A. Current SCR Systems Are Highly Effective in Use
As trucks equipped with SCR systems have been introduced into U.S.
commerce, drivers have become familiar with this technology. Current
information concerning in use operation of SCR-equipped trucks,
including all of the studies and other information discussed above,
indicates that warning signals work correctly and that drivers do not
wait for SCR-related inducements to be triggered to ensure appropriate
and continuing operation of the systems. Specifically, the overwhelming
majority of drivers surveyed by CARB, ATA, and Cummins did not wait for
activation of warning indicators prior to refilling their DEF tanks
and, where warnings did occur, generally did not drive distances long
enough to lead to activation of inducements. Further, as the
infrastructure for making DEF available becomes even more widespread,
drivers will have increased and more convenient access to DEF when they
need it. As documented in part by CARB's survey, there are currently
few availability issues and those appear to stem primarily from limited
situations where DEF was not found at the first location at which it
was sought. As DEF infrastructure and supply continue to expand, EPA
also expects the price of DEF to decrease, in part because of the move
to bulk dispensing that is already underway. In addition, EPA expects
that the DEF quality assurance programs described above will make it
increasingly easy for drivers to find DEF which meets the
specifications necessary for proper operation of the SCR systems. The
strong indication from all of this evidence is that DEF warning systems
are working correctly, and that when warned, drivers have not continued
to drive distances long enough to lead to inducements. Inducements
appear to be triggered in very few cases.
Navistar's study and CARB's field evaluation provide some evidence
indicating that in some cases there have been issues related to SCR-
equipped engines and assurance of their proper operation. Navistar's
study identifies specific problems associated with the design or
manufacture of certain SCR-equipped engines, and outlines the
intentional actions taken by drivers employed by Navistar's contractor
in conducting the study. The study's findings are properly considered
in the context of all the available information on SCR operation. In
light of the investigations and surveys conducted by CARB, ATA, and
Cummins, EPA does not believe Navistar's findings reflect the overall
efficacy of SCR systems on heavy-duty diesel engines currently in
operation or the way they are actually used.
Most of Navistar's findings resulted from actions by the
contractor's drivers to intentionally circumvent the manufacturer-
designed inducements of the three test vehicles. For example, drivers
avoided triggering inducements associated with an empty DEF tank by
limiting refueling quantities or keeping the truck running when it
normally would be turned off. Both ways of circumventing the
inducements exact their own costs on drivers in terms of time,
convenience, and expense. To illustrate, never refilling above about
30% of the tank leads to approximately three times as many refueling
events, and the time and expense associated with this kind of
disruption detract from the efficient operation of truck operators, who
work in a competitive business. Navistar's contract drivers also
disconnected and reconnected various SCR system components as a means
of avoiding DEF inducements. Such intentional actions would be
considered tampering and are illegal.\19\ While it is possible that
drivers could intentionally take such actions to circumvent
inducements, manner of truck operation conducted in the Navistar study
is clearly not representative of the vast majority of truck operation,
as indicated by the CARB and ATA surveys. We do not think that the
marginal cost and effort involved in purchasing DEF provide sufficient
motivation for a driver to follow such inconvenient and risky courses
of action.
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\19\ Such actions are illegal, unless conducted as part of a
testing program covered by an Agency-issued testing exemption.
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We also do not agree with Navistar's view that initial inducements
are ineffective to produce corrective responses by drivers. ATA's fleet
survey indicates that drivers do not favor inducements involving an
engine power derate, especially if it occurs while a truck under heavy
load is driving up-hill. Thus, drivers are likely to maintain proper
SCR operation to avoid encountering these inducements. CARB's
investigation shows that most inducements functioned properly during
expected truck operating conditions and their assessment of the
effectiveness of initial inducements was contrary to Navistar's
findings. CARB determined that the inducements were effective because
operating in a way that avoids the inducement strategies and raise the
risk of costly repairs would not be worth the downtime and potential
financial loss to business. In fact, Cummins' survey, which included
some of the same 15-liter engines in Navistar's study, found that
surveyed trucks operated with DEF in their tanks for greater than 99.9
percent of their total operation. Cummins' survey also found that
trucks operated with unacceptable DEF quality for less than 0.18
percent of their total operation. This strongly indicates that the
inducements have the intended effect of motivating appropriate driver
behavior.
The report of Navistar's study found that some manufacturers'
designs did not adequately detect water in the urea tank and thus did
not prevent the driver from refilling the tank with something other
than DEF. Navistar and CARB findings on DEF quality detection were not
consistent in all cases. For example, Navistar found that initial and
final inducements for the Freightliner Cascadia equipped with the 12.8-
liter Detroit Diesel DD13 engine were not triggered when the DEF tank
was filled with water. During CARB's field investigation, both the
initial and final inducements were implemented for Test
[[Page 32893]]
Vehicle 1 as expected when the DEF tank was filled with water. CARB's
investigation discovered various production defects for Test Vehicles 2
and 3 that prevented the systems from working fully (as designed, the
systems appeared to have sufficient capabilities to detect and respond
to DEF quality problems). CARB followed up with Cummins and learned
that the manufacturer was aware of the performance problems and
addressing them in a manner consistent with regulatory provisions
governing defect reporting and repair.\20\ The defect reports submitted
by Cummins corroborated that the manufacturer was appropriately
responding to the problems. Additionally, Detroit Diesel informed EPA
that they knew of problems with their system and had developed an
updated software calibration to fix them as early as June 2010, prior
to Navistar reporting the results of their study. Detroit Diesel has
since begun addressing the problems on in use trucks consistent with
regulatory provisions governing defect reporting and repair. As noted
above, the problems with detecting water in the urea tank appear to be
related to defects in production of these engines, as opposed to
deficient designs. These production defects are being addressed in the
same manner that problems with new technology are addressed under EPA's
regulations.
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\20\ See 40 CFR Part 85, Subpart T.
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B. Regulations Should Be Applied in Light of Continuing Information and
Process Improvements
EPA's regulatory provisions for adjustable parameters are intended
to ensure that manufacturers design their emissions control system in a
way that makes it unlikely that they will be operated inappropriately.
It appears that manufacturer's past SCR designs and EPA's guidance have
resulted in highly effective controls to protect the operation of SCR
systems, as evidenced by the surveys and other data which show that
drivers are properly operating their SCR-equipped trucks. There have
been indications of specific problems with some engines in-use, and the
manufactures involved have been addressing them through production and
other improvements as the problems are identified. We believe it is
appropriate to evaluate the experience gained to date and to make
continuing, appropriate adjustments to our certification process for
SCR-equipped engines as technology evolves and in-use experience is
gained. EPA recognizes that development of even more robust sensors and
inducements does not negate past approaches implemented pursuant to
existing regulations. Rather, continual improvement is expected given
the mounting experience with, and the maturing of, SCR technology, and
the greater availability of DEF. As improved strategies and
capabilities for proper SCR operation become feasible, EPA may guide
their application to provide even further assurance that the technology
is operating as intended on SCR-equipped engines.
C. As SCR Technology Matures, Further Guidance Is Appropriate
Several developments in SCR technology allow continuing refinement
in SCR design. One area of potential improvement in design involves
sensors that can detect poor quality DEF. Current SCR system designs
incorporate NOX sensors to determine catalyst efficiency and
detect catalyst malfunction. Since the sensors are part of the system
design, they have also been used to detect poor quality DEF through
correlation of NOX emission rates with various
concentrations of urea. Urea quality sensors have been identified as a
means to help improve detection capabilities for poor quality urea.
They directly measure quality and appear likely to represent a quick
detection method for addressing quality concerns. Manufacturers are
currently evaluating the performance and durability of various sensor
designs.
Since the 2010 model year, manufacturers have also been refining
their engine/vehicle system diagnostics software to incorporate
additional capabilities for implementing SCR-related inducements. For
example, many manufacturers today have developed multiple triggers for
triggering inducements, including detection of refueling, extended
idling, and engine shutdown events. Incorporation of additional
inducement triggers into designs further decreases the likelihood of
improper operation of the SCR system. Manufacturers are also improving
their diagnostics software to ensure that SCR-related inducements
cannot be reset or erased by diagnostic scan tools available to the
general public or by disconnecting components in the field.
Many manufacturers are implementing improved designs in their 2011
model year engines/trucks that may be sold in the State of California.
After the July 2010 public workshop, CARB and EPA began encouraging
manufacturers to adopt the elements of design that were discussed. In
order to avoid the need for multiple engine/vehicle production designs,
manufacturers have often incorporated the design elements of vehicles
sold in California into their 49-state vehicles.
Improving sensor capabilities and inducement strategies should
present low risk and little burden for both manufacturers and drivers.
Manufacturers are already in the process of improving their SCR
designs, and overwhelmingly drivers are not waiting for SCR-related
warnings or inducements to be triggered before they refill DEF tanks
and otherwise maintain proper operation of SCR systems. Given the
importance of reducing NOX emissions from heavy-duty diesel
engines for attaining and maintaining national air quality standards,
we have developed the following draft revised guidance to reflect
improving capabilities for designing SCR systems to ensure proper
operation.
VII. SCR Adjustable Parameter Design Criteria
This section discusses design criteria for on-highway heavy-duty
diesel vehicles or engines using SCR technology. EPA believes that
vehicles and engines that meet these design criteria would meet the
requirements of the regulations regarding adjustable parameters. EPA
will still review each certification application to ensure that the
regulatory provisions are met. Likewise, in the case of design criteria
that are not fully specified in this guidance, EPA will review the
application to ensure that the engine design meets the regulatory
requirements. EPA may review and revise this guidance as the technology
continues to mature and as EPA receives more information regarding the
use of SCR systems. In addition, manufacturers may present other
designs for EPA consideration. All designs will remain subject to EPA
approval under the existing certification regulations.
As noted above, in determining the adequacy of an engine's means of
inhibiting adjustment of a parameter, EPA considers the likelihood that
settings other than the manufacturer's recommended setting will occur
in use. With this in mind, EPA is providing these draft SCR adjustable
parameter design criteria based on our view that an SCR-equipped
vehicle that complies with these criteria will be adequately inhibited
from use when the SCR system is not operating properly.
EPA is asking for comments on the draft guidance discussed below.
The design criteria are divided into four categories. The categories
are:
A. Reductant tank level driver warning system.
[[Page 32894]]
B. Reductant tank level driver inducement.
C. Identification and correction of incorrect reducing agent.
D. Tamper resistant design.
A. Reductant Tank Level Warning System
The emissions performance of SCR-equipped vehicles depends on
having an adequate supply of appropriate quality reducing agent in the
system. SCR systems require regular user interaction to ensure that the
system is operating properly. Therefore, it is critical that the
operator both know when reducing agent is needed and have enough time
to replace it before it runs out. A properly designed driver warning
system should address these concerns.
To achieve this design goal, under our criteria, the manufacturers
would use a warning system including the following features:
1. The warning system should incorporate visual and possibly
audible alarms informing the vehicle operator that reductant level is
low and must soon be replenished. The manufacturer should design the
warning system to activate well in advance of the reducing agent
running out so that the operator is expected to have one or more
refueling opportunities to refill the reductant tank before it is
empty.
2. The warning alarm(s) should escalate in intensity as the
reducing agent level approaches empty, culminating in driver
notification that is difficult to ignore, and cannot be turned off
without replenishment of the reducing agent.
3. To provide adequate notice, the visual alarm should, at a
minimum, consist of a DEF level indicator, a unique light, reducing
agent indicator symbol or message indicating low reducing agent level.
The warning light, symbol or message should be different from the
``check engine'' or ``service engine soon'' lights used by the On Board
Diagnostic (OBD) system or other indicators that maintenance is
required. The symbol or message used as the warning indicator should
unmistakably indicate to the vehicle operator that the reducing agent
level is low. The reducing agent indicator symbol shown below has been
generally accepted in the industry and EPA considers it acceptable as
an indicator of low reducing agent level.
[GRAPHIC] [TIFF OMITTED] TP07JN11.008
4. The light, indicator symbol or message should be located on the
dashboard or in a vehicle message center. The warning light or message
does not initially have to be continuously activated, but as the
r