Lead; Clearance and Clearance Testing Requirements for the Renovation, Repair, and Painting Program, 47918-47946 [2011-19417]
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Federal Register / Vol. 76, No. 151 / Friday, August 5, 2011 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 745
[EPA–HQ–OPPT–2005–0049; FRL–8881–8]
RIN 2070–AJ57
Lead; Clearance and Clearance Testing
Requirements for the Renovation,
Repair, and Painting Program
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
As part of a settlement of
litigation over certain post-renovation
cleaning requirements of the 2008 Lead
Renovation, Repair, and Painting
Program (RRP) rule, the EPA agreed to
propose a number of revisions to the
2008 RRP rule that established
accreditation, training, certification, and
recordkeeping requirements as well as
work practice standards for persons
performing renovations for
compensation in most pre-1978 housing
and child-occupied facilities and to
subsequently take final action on the
proposed rule by July 15, 2011. The
proposed rule published on May 6,
2010. EPA has decided not to
promulgate dust wipe testing and
clearance requirements as proposed.
However, EPA is promulgating several
other revisions to the RRP rule,
including a provision allowing a
certified renovator to collect a paint
chip sample and send it to a recognized
laboratory for analysis in lieu of using
a lead test kit, minor changes to the
training program accreditation
application process, standards for elearning in accredited training
programs, minimum enforcement
provisions for authorized state and
tribal renovation programs, and minor
revisions to the training and
certification requirements for
renovators. EPA is also promulgating
clarifications to the requirements for
vertical containment on exterior
renovation projects, the prohibited or
restricted work practice provisions, and
the requirements for high-efficiency
particulate air (HEPA) vacuums.
Today’s action is EPA’s final action on
all aspects of the May 6, 2010 proposal.
DATES: This final rule is effective
October 4, 2011.
ADDRESSES: EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPPT–2005–0049. All documents in the
docket are listed in the docket index
available at https://www.regulations.gov.
Although listed in the index, some
information is not publicly available,
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SUMMARY:
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e.g., Confidential Business Information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy. Publicly
available docket materials are available
in the electronic docket at https://
www.regulations.gov, or, if only
available in hard copy, at the OPPT
Docket. The OPPT Docket is located in
the EPA Docket Center (EPA/DC) at Rm.
3334, EPA West Bldg., 1301
Constitution Ave., NW., Washington,
DC. The EPA/DC Public Reading Room
hours of operation are 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding
legal holidays. The telephone number of
the EPA/DC Public Reading Room is
(202) 566–1744, and the telephone
number for the OPPT Docket is (202)
566–0280. Hearing- or speech-impaired
persons may reach the above telephone
numbers through TTY by calling the
toll-free Federal Relay Service at 1–800–
877–8339. Docket visitors are required
to show photographic identification,
pass through a metal detector, and sign
the EPA visitor log. All visitor bags are
processed through an X-ray machine
and subject to search. Visitors will be
provided an EPA/DC badge that must be
visible at all times in the building and
returned upon departure.
FOR FURTHER INFORMATION CONTACT: For
technical information contact: Cindy
Wheeler, National Program Chemicals
Division (7404T), Office of Pollution
Prevention and Toxics, Environmental
Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460–
0001; telephone number: (202) 566–
0484; e-mail address:
wheeler.cindy@epa.gov.
For general information contact: The
TSCA-Hotline, ABVI–Goodwill, 422
South Clinton Ave., Rochester, NY
14620; telephone number: (202) 554–
1404; e-mail address: TSCAHotline@epa.gov. Hearing- or speechimpaired persons may reach the above
telephone number through TTY by
calling the toll-free Federal Relay
Service at 1–800–877–8339.
SUPPLEMENTARY INFORMATION:
I. Does this action apply to me?
You may be potentially affected by
this action if you perform renovations of
target housing or child-occupied
facilities for compensation, dust
sampling, or dust testing. You may also
be affected by this action if you perform
lead-based paint inspections, lead
hazard screens, risk assessments or
abatements in target housing or childoccupied facilities or if you operate a
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training program for individuals who
perform any of these activities. ‘‘Target
housing’’ is defined in section 401 of
TSCA as any housing constructed prior
to 1978, except housing for the elderly
or persons with disabilities (unless any
child under age 6 resides or is expected
to reside in such housing) or any 0bedroom dwelling. Under this rule, a
child-occupied facility is a building, or
a portion of a building, constructed
prior to 1978, visited regularly by the
same child, under 6 years of age, on at
least 2 different days within any week
(Sunday through Saturday period),
provided that each day’s visit lasts at
least 3 hours and the combined weekly
visits last at least 6 hours, and the
combined annual visits last at least
60 hours.
Potentially-affected entities may
include, but are not limited to:
• Building construction (NAICS code
236), e.g., single family housing
construction, multi-family housing
construction, residential remodelers.
• Specialty trade contractors (NAICS
code 238), e.g., plumbing, heating, and
air-conditioning contractors, painting
and wall covering contractors, electrical
contractors, finish carpentry contractors,
drywall and insulation contractors,
siding contractors, tile and terrazzo
contractors, glass and glazing
contractors.
• Real estate (NAICS code 531), e.g.,
lessors of residential buildings and
dwellings, residential property
managers.
• Child day care services (NAICS
code 624410).
• Elementary and secondary schools
(NAICS code 611110), e.g., elementary
schools with kindergarten classrooms.
• Other technical and trade schools
(NAICS code 611519), e.g., training
providers.
• Engineering services (NAICS code
541330) and building inspection
services (NAICS code 541350), e.g., dust
sampling technicians.
• Lead abatement professionals
(NAICS code 562910), e.g., firms and
supervisors engaged in lead-based paint
activities.
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
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the technical person listed under FOR
FURTHER INFORMATION CONTACT.
II. Background
A. What action is the agency taking?
On May 6, 2010, EPA proposed a
number of revisions to the 2008 Lead
Renovation, Repair, and Painting
Program (RRP) rule that established
accreditation, training, certification, and
recordkeeping requirements as well as
work practice standards for persons
performing renovations for
compensation in most pre-1978 housing
and child-occupied facilities (Ref. 1).
Specifically, EPA proposed
requirements for dust wipe testing,
clearance, allowing a certified renovator
to collect a paint chip sample and send
it to a recognized laboratory for analysis,
minor changes to the training program
accreditation application process,
standards for e-learning in accredited
training programs, minimum
enforcement provisions for authorized
state and tribal renovation programs,
and minor revisions to the training and
certification requirements for
renovators. EPA has decided not to
promulgate dust wipe testing and
clearance requirements as proposed.
However, EPA is promulgating several
of the other proposed revisions to the
RRP rule, including a provision
allowing a certified renovator to collect
a paint chip sample and send it to a
recognized laboratory for analysis in
lieu of using a lead test kit, minor
changes to the training program
accreditation application process,
standards for e-learning in accredited
training programs, minimum
enforcement provisions for authorized
state and tribal renovation programs,
and minor revisions to the training and
certification requirements for
renovators. EPA is also promulgating
clarifications to the requirements for
vertical containment on exterior
renovation projects, the prohibited or
restricted work practice provisions, and
the requirements for high-efficiency
particulate air (HEPA) vacuums.
Today’s action is EPA’s final action on
all aspects of the May 6, 2010 proposal.
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B. What is the agency’s authority for
taking this action?
These work practice, training,
certification and accreditation
requirements, and the State, Territorial
and Tribal authorization provisions are
being promulgated under the authority
of sections 402(c)(3), 404, and 407 of the
Toxic Substances Control Act (TSCA),
15 U.S.C. 2682(c)(3), 2684, and 2687.
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C. What are the specific provisions of
this action?
1. Clearance and dust wipe testing
requirements for renovations. As
discussed in this unit, EPA has decided
not to promulgate clearance and dust
wipe testing requirements as proposed
in May 2010 for certain renovations
covered by the 2008 Lead Renovation,
Repair, and Painting (RRP) rule (Ref. 2).
a. Background. In promulgating the
final 2008 RRP rule, EPA determined
that renovation, repair, and painting
activities, when performed in the
presence of lead-based paint, create
lead-based paint hazards. Section
402(c)(3) of TSCA directs EPA to revise
its regulations governing lead-based
paint inspections, risk assessments, and
abatements (the Lead-based Paint
Activities Regulations, or abatement
regulations, Ref. 3) to apply to
renovation and remodeling activities
that create lead-based paint hazards.
Accordingly, the 2008 RRP rule
established accreditation, training,
certification, and recordkeeping
requirements as well as work practice
standards for persons performing
renovations for compensation in most
pre-1978 housing and child-occupied
facilities. Among other things, the work
practice standards require renovation
firms to follow specific requirements for
containing the work area, refrain from
using certain high-dust-generating work
practices, and follow a specific cleaning
protocol, including a step called
‘‘cleaning verification,’’ after concluding
the paint-disturbing tasks involved in a
renovation.
As discussed in the preamble to the
2010 proposal, EPA is particularly
concerned about dust-lead hazards
generated by renovations because of the
well-documented toxicity of lead,
especially to younger children. For a
more detailed discussion of the health
effects of lead exposure, refer to
information in the 2010 proposal (Ref.
1) and the 2008 RRP final rule (Ref. 2).
One of the more difficult issues in the
2008 RRP rulemaking was the issue of
determining when a renovation work
area has been properly cleaned and is
ready for reoccupancy. After a leadbased paint abatement project, EPA’s
Lead-Based Paint Activities Regulations
require the abatement contractor to
achieve clearance. This means that the
contractor must demonstrate, through
dust wipe testing, that dust lead levels
remaining in the abatement work area
are below the clearance levels
established in the 2001 rulemaking
entitled ‘‘Identification of Dangerous
Levels of Lead’’ under section 403 of the
Toxic Substances Control Act (Ref. 4).
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Dust wipe samples for clearance
purposes must be collected by a
certified individual and analyzed by an
entity recognized under the National
Lead Laboratory Accreditation Program
(NLLAP).
When promulgating the 2008 RRP
rule, EPA considered requiring a similar
process after renovations, but for
various reasons, did not do so. EPA did
not interpret its statutory mandate
under TSCA section 402(c)(3) as simply
expanding the scope of the Lead-based
Paint Activities Regulations to also
cover renovation activities. Rather, EPA
stated, in the final 2008 RRP rule, its
belief that Congress intended for EPA to
make revisions to those existing
regulations to adapt them to a different
set of activities and a very different
regulated community. In establishing
the cleaning element of the work
practice requirements for renovations,
EPA primarily relied on the results of
two studies, the ‘‘Electrostatic Cloth and
Wet Cloth Field Study in Residential
Housing’’ (Ref. 5) and the
‘‘Characterization of Dust Lead Levels
after Renovation, Repair, and Painting
Activities’’ (the ‘‘Dust Study,’’ Ref. 6) to
determine that the full suite of RRP
work practice requirements, including
containment, cleaning, and cleaning
verification, was effective at minimizing
exposure to lead-based paint hazards
created by renovation, repair, and
painting activities.
EPA also considered various other
factors as well as issues raised by
commenters. Among these were the
differences between abatement and
renovation, the costs of dust wipe
testing and clearance, the potential
delay in obtaining results, and the
likelihood that renovation firms would
become liable for pre-existing dust-lead
hazards. Abatements have only one
purpose, to permanently eliminate leadbased paint or lead-based paint hazards,
while renovations are performed for
many reasons that often have nothing to
do with lead-based paint. Concerns
about the costs of dust wipe testing and
clearance were brought to EPA’s
attention during stakeholder input
opportunities provided by EPA before
the proposed RRP rule was issued in
2006 and echoed by commenters on the
2006 proposed RRP rule. If EPA had
required dust wipe testing and clearance
after every renovation project, it would
have made up a significant portion of
the cost of smaller projects. In addition,
dust wipe testing results may not be
available for several days. If EPA had
required traditional abatement-style
clearance after renovations, the work
area would not be able to be re-occupied
while waiting for the laboratory results.
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Commenters also noted that requiring
clearance after renovation jobs could, in
some instances, result in the renovation
firm being held responsible for abating
all dust-lead hazards, including such
hazards that may have existed in the
area before the renovation commenced.
Other commenters on the 2006
proposed RRP rule thought that
renovation work areas ought to be tested
and cleared for re-occupancy in the
same way that abatement work areas are
cleared through the clearance process,
including dust wipe testing. Many
commenters believed that renovation
firms should be required to demonstrate
that no dust-lead hazards had been left
behind in the work area. These
commenters contended that the only
effective way to do this is through dust
wipe testing and clearance. While EPA
understood the issues raised by these
commenters, and agreed with some of
the points that they made, EPA
remained convinced that the suite of
RRP work practices would be practical
for renovation firms to implement while
effectively minimizing exposure to dustlead hazards created by renovations.
The RRP work practices are, in essence,
requirements to ensure that renovators
undertake traditional renovation
activities—e.g., removal or modification
of existing surfaces, containment and
cleanup of dust and debris, and
ensuring the job site is cleaned up—in
a lead-safe way. EPA believes the RRP
rule effectively minimizes exposure to
hazards generated by renovation
activities without imposing practices
and disciplines that are outside the
scope of traditional renovation
activities. More information on the
comments received and EPA’s decisions
can be found in the preamble to the
final 2008 RRP rule (Ref. 2).
b. 2010 Proposal. Based on additional
stakeholder input received after the
final rule was issued, and an August
2009 agreement entered into with
several environmental and children’s
health advocacy groups in settlement of
their lawsuit challenging the final 2008
RRP rule, EPA agreed to consider
whether some of the decisions made in
2008 with regard to dust wipe testing
and clearance should be modified.
Accordingly, on May 6, 2010, EPA
proposed to require dust wipe testing
after many renovations covered by the
RRP rule (Ref. 1). Under the 2010
proposal, dust wipe testing would have
been required on uncarpeted floors,
windowsills, and window troughs in the
work area after the following types of
interior renovations:
• Use of a heat gun at temperatures
below 1100 degrees Fahrenheit.
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• Removal or replacement of window
or door frames.
• Scraping 60 ft2 or more of painted
surfaces.
• Removing more than 40 ft2 of trim,
molding, cabinets, or other fixtures.
After these renovations, the
renovation firm would have been
required to collect dust wipe samples
and have them analyzed for lead content
by an entity recognized under NLLAP.
The renovation firm would then have
been required to provide these results to
the owners and occupants of the
renovated property.
For another subset of jobs involving
demolition or removal of plaster
through destructive means or the
disturbance of paint using machines
designed to remove paint through highspeed operation, such as power sanders
or abrasive blasters, EPA proposed to
require the renovation firm to achieve
clearance. This would have involved a
demonstration, through dust wipe
testing, that dust-lead levels remaining
on uncarpeted floors, windowsills, and
window troughs in the work area were
below regulatory clearance levels. These
clearance levels would have been
identical to the clearance levels
established for the lead-based paint
abatement program, which are codified
at 40 CFR 745.227(e)(8)(viii), i.e., 40 μg/
ft2 on floors, 250 μg/ft2 on interior
windowsills, and 400 μg/ft2 on window
troughs, based on wipe samples. These
additional requirements in the 2010
proposal were designed to ensure that
lead-based paint hazards generated by
renovation work are adequately cleaned
after renovation work is finished and
before the work areas are re-occupied.
c. This final rule. Maintaining the
distinction between abatement and
renovation activities has been an
important issue throughout the
rulemaking process for the 2008 RRP
rule. As discussed in the preamble to
the 2008 RRP rule, abatements and
renovations are performed by different
contractors for different purposes,
although similar activities, such as
window replacements, may be involved.
Typically, when an abatement is
performed, the housing is either
unoccupied or the occupants are
temporarily relocated to lead-safe
housing until the abatement has been
demonstrated to have been properly
completed through the clearance
process. Carpet in the housing is usually
removed as part of the abatement
because it is difficult to demonstrate
that it is free of lead-based paint
hazards. Uncarpeted floors that have not
been replaced during the abatement may
need to be refinished or sealed in order
to achieve clearance. Abatements have
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only one purpose—to permanently
eliminate lead-based paint and leadbased paint hazards. In contrast,
renovations other than interim controls
are performed for reasons unrelated to
lead-based paint or lead-based paint
hazards. Renovations may be performed
while the property is occupied or
unoccupied, but occupants do not
typically relocate pending the
completion of the project.
EPA did not design or intend the RRP
rule to address cleanup of pre-existing
dust-lead hazards. While the cleaning
requirements of the RRP rule will, in
some cases, have the ancillary benefit of
removing some pre-existing dust-lead
hazards, the cleaning requirements were
designed to effectively clean-up leadbased paint hazards created during
renovation activities without changing
the scope of the renovation activity
itself. Accordingly, the RRP rule does
not require cleaning of dust or any other
possible lead sources in portions of
target housing or child-occupied
facilities beyond locations in and
around the work area. Nor does the RRP
rule require the replacement of carpets
in the area of the renovation or the
refinishing or sealing of uncarpeted
floors. The approach in the RRP rule
was designed to address the lead-based
paint hazards created during the
renovation while not requiring
renovation firms to remediate or
eliminate hazards beyond the scope of
the work they were hired to do.
In addition, EPA has interpreted
practicality in implementation to be an
element of the statutory directive to take
into account effectiveness and
reliability. As discussed in the preamble
to the final 2008 RRP rule, EPA believes
that, given the highly variable nature of
the regulated community, the work
practices required by the RRP rule
should be simple to understand and
easy to use. EPA is cognizant of the fact
that the RRP rule applies to a range of
individuals from day laborers to
property maintenance staff to master
craftsmen performing a range of
activities from simple drywall repair to
window replacement to complete
kitchen and bath renovations to
building additions and everything in
between. Work practices that are easy
and practical to use are more likely to
be followed by all of the persons who
perform renovations, and, therefore,
more likely to be reliable and effective
in minimizing exposure to lead-based
paint hazards created by renovation
activities.
The 2010 proposal for this rule was
EPA’s attempt to explore whether
clearance and dust wipe testing
requirements should be added to the
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RRP rule to provide additional
protection for some renovations. EPA’s
intention was to do this without
generally holding renovation firms
responsible for abating pre-existing
dust-lead hazards or creating
requirements that would impair the
overall reliability and effectiveness of
the work practice requirements.
EPA received over 300 comments on
its 2010 proposal. Members of the
regulated community and other industry
commenters were generally concerned
that EPA had upset the balance it had
struck in the 2008 RRP rule, arguing that
a dust wipe testing or clearance
requirement would have the effect of
holding renovation firms responsible for
pre-existing hazards, whether directly
by regulation, in the case of the
proposed clearance requirements, or
indirectly by requiring firms to provide
information on post-renovation dust
lead levels to the property owner and
occupant. While there was little support
for dust wipe testing alone, commenters
that supported the 2010 proposal
generally thought that a clearance
requirement should be imposed and
expanded to most, if not all,
renovations.
After carefully weighing the issues at
stake and considering the concerns
raised by commenters, and as explained
in greater detail below, EPA has
concluded that, on balance, the
information before the Agency does not
support imposing a dust wipe testing or
clearance requirement on renovations.
In particular, EPA is convinced that the
work practices established in the 2008
RRP rule are reliable, effective, and safe,
and that imposing a dust wipe testing or
clearance requirement is unwarranted.
Almost all of the commenters were
opposed to the proposed provisions
requiring only dust wipe testing after
certain renovations. Members of the
regulated community and other industry
commenters argued that a dust wipe
testing requirement would have the
effect of holding renovation firms
responsible for pre-existing hazards,
albeit indirectly, by requiring firms to
provide information on post-renovation
dust lead levels to the property owner
and occupant. This requirement would
also have the effect of adding an
element that is not generally considered
a renovation activity, i.e., taking
samples for laboratory analysis, and
indeed, would have to be performed by
a third party or only after a renovator
received training in a separate and
distinct discipline—either as a dust
wipe sample technician or a lead-based
paint inspector. In addition, many
argued that the Dust Study generally
shows that the RRP work practices are
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effective at minimizing occupant
exposure to dust-lead hazards created
by renovations, so additional dust wipe
testing or clearance requirements are
unnecessary. These commenters noted
that this is particularly true for the
renovations for which EPA proposed to
require only dust wipe testing, because
those renovations were specifically
tested in the Dust Study. In addition,
commenters suggested that the
categories of jobs for which dust wipe
testing or clearance would be required
were arbitrary and not based on
sufficient evidence.
Some commenters, including several
states, also questioned the utility and
value of dust wipe testing in the absence
of a clearance requirement. Some were
concerned that property owners and
occupants would not understand the
significance of the results of dust wipe
samples that exceed the clearance
standards or what steps they should
take to protect themselves and their
families. One argued that, in the absence
of standards and required remedial
actions, dust wipe testing would add
expense and time to a renovation project
without providing a concrete increase in
protection for occupants. On the other
hand, other commenters contended that
the feedback provided by numerical
dust wipe testing results would result in
improved cleaning performance on the
part of renovation firms. Some cited
anecdotal evidence of poor contractor
performance in other programs, such as
the abatement program, in support of a
contention that the RRP rule work
practices would not be as effective at
minimizing dust-lead hazards as they
were in the Dust Study.
Additionally, after considering
previous interpretations of the statutory
requirements and the comments
received on this specific issue, EPA is
not convinced that dust wipe testing in
the absence of a clearance requirement
would be a safe, reliable and effective
work practice within the meaning of
TSCA Section 402. As commenters
noted, provision of dust wipe testing
results in the absence of a clearance
requirement does not by itself reduce
the amount of dust generated during or
left behind following a renovation.
Furthermore, dust wipe testing results
alone are not part of the information
that must be provided at the prerenovation stage under Section 406(b) of
TSCA, and providing this type of
information is not typically considered
a renovation work practice. Again, the
dust wipe testing would either have to
be done by a third party or by a
renovator who has taken a course and
been trained in a completely different
discipline.
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EPA believes these commenters raise
valid considerations. In particular, EPA
agrees that the Dust Study demonstrates
that with respect to these very activities,
the suite of RRP work practices reliably
addressed the hazards created by the
renovation. In addition, although EPA
attempted in its 2010 proposal to
distinguish renovation activities that it
thought warranted the addition of a dust
wipe testing requirement from those
that did not (and from those that
warranted imposition of a clearance
requirement), EPA acknowledges that its
2010 proposal lacked a strong basis for
drawing these lines—a point made by
many commenters. While some
commenters urged the point that dust
wipe testing would encourage better
cleanup, and provided anecdotal
support for that view, EPA has no
record basis to judge the likelihood or
frequency of this potential impact. This
logic could potentially lead to requiring
dust wipe testing for all jobs—a
significant change in the existing rule
that EPA is not prepared to make
without better supporting evidence.
Accordingly, upon the information
before it, the Agency does not believe
that a dust testing requirement alone is
warranted. EPA notes that homeowners
can arrange to have dust wipe testing
done as part of a renovation (or at any
time) if they would like information
about dust-lead levels in their homes.
EPA also notes that property owners can
contractually elect clearance testing at
the completion of a project. EPA’s Web
site has a page homeowners can use to
locate certified lead inspection and
abatement professionals and accredited
training providers in their state (https://
www.epa.gov/lead/pubs/locate.htm).
EPA also proposed to require that
renovation firms achieve clearance for a
subset of jobs involving demolition or
removal of plaster through destructive
means or the disturbance of paint using
machines designed to remove paint
through high-speed operation, such as
power sanders or abrasive blasters.
Nonetheless, EPA remained concerned
about promulgating a requirement that
could make renovation firms
responsible for pre-existing conditions
and fundamentally change the scope of
the renovation activity itself. Therefore,
to avoid making renovation firms
replace carpets or refinish floors when
they were not hired to do so, EPA
proposed to allow a renovation firm to
stop after two failed dust wipe tests on
a particular surface if the firm was not
hired to refinish or replace that surface.
EPA was particularly concerned about
these types of jobs because it had
evidence that the work practices were
not effective when machines designed
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to remove paint through high speed
operation were operated without HEPA
shrouds and created large quantities of
dust. EPA was concerned that even if
such machines were equipped with
HEPA shrouds, the RRP work practices
may not be effective at minimizing
exposure to lead hazards created by the
renovation. Additionally, EPA stated its
belief that dust created by the
demolition or removal of plaster was
similarly difficult to clean and therefore
the RRP work practices might not be
effective at minimizing exposure to lead
hazards created by the renovation.
With respect to the proposed
clearance requirements, commenters
generally fell into two camps.
Commenters who were in ‘‘favor’’ of the
2010 proposal nonetheless generally
argued that the proposed clearance
requirements should be expanded to
cover most if not all renovation
activities because clearance is the only
method to ensure that no lead hazards
remain upon the completion of a
renovation job. Commenters who
opposed any type of clearance
requirement argued again that it erased
the distinction between renovations and
abatements and made renovation firms
responsible for pre-existing conditions.
These commenters also questioned the
relevance of the studies EPA cited in
support of its 2010 proposal to require
clearance after renovations involving
demolition or removal of plaster
through destructive means or the
disturbance of paint using machines
designed to remove paint through highspeed operation. The cited studies
include EPA’s Environmental Field
Sampling Study (EFSS, Ref. 7) and
studies examining the effectiveness of
HEPA exhaust control on power tools
(Ref. 8). Many of the HEPA exhaust
control studies addressed dusts not
typically created during renovations
regulated by the RRP rule, such as
crystalline silica dust resulting from the
grinding of concrete. Others addressed
surfaces and surface coatings not
typically encountered during
renovations covered by the RRP rule;
one involved paint removal from
automobiles. Notwithstanding EPA’s
2010 proposal and requests for
comment, EPA did not receive any
additional information or data with
respect to the dust or hazards created by
these activities. Finally, on both sides of
the issue, commenters did not favor the
proposed provision allowing renovation
firms to stop after two failed dust wipe
tests, and, although some alternative
suggestions were offered, none
effectively addressed the competing
considerations of occupant protection
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and not expanding the scope of the
renovation work.
EPA recognizes that imposing a
clearance requirement would be a
departure from the balance struck in the
RRP rule with respect to the distinction
between abatement and renovations.
Accordingly, in EPA’s judgment, the
Agency should be in a position to
conclude with a fair amount of certainty
that doing so was necessary in light of
its obligation to promulgate work
practices that take into account
reliability, effectiveness, and safety.
Here, EPA acknowledges that it does not
have data to support its concern that
dust created by destructive demolition
of plaster may be similar in nature to
dust generated by machines designed to
remove paint through high speed
operation, and thus would have the
potential to overwhelm the RRP
cleaning protocol. EPA also recognizes
that the data on the efficiency of HEPA
is only suggestive that there might be an
issue concerning these practices. Again,
the studies EPA reviewed suggested that
HEPA exhaust control could reduce the
airborne dust levels by 90–95%. As
commenters pointed out, it is not clear
the results of these studies are
applicable to the home renovation
setting, given the differences between
the surfaces and paints in residential
settings and the surfaces and paints
involved in the studies. Even if the
results were applicable, there is no
direct evidence that the RRP lead safe
work practices could not reliably
address the dust hazards created by the
use of such power tools. Having
received no additional information in
this regard, EPA has determined that,
among other things, the available
information does not support a
clearance requirement. Nevertheless, as
discussed further in Unit II.C.7. of this
preamble, EPA is adding a requirement
that power tools be operated so that no
visible dust or release of air occurs
outside of the shroud or containment
system. This requirement will work to
mitigate the concerns EPA had with
respect to the efficiency of power tool
dust collection systems and the
possibility that such tools might
overwhelm the containment and
specialized cleaning protocols of the
RRP work practices.
In an effort to ensure that the
proposed clearance requirement would
not typically result in holding
renovation firms responsible for abating
pre-existing dust-lead hazards, EPA
included a provision to allow firms to
stop the clearance procedure after two
failed clearance tests on a particular
surface unless they had also contracted
to refinish the surface. Upon further
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reflection, EPA is concerned about the
potential ineffectiveness of this effort,
because it would likely still result in
some renovation firms having to clean
up pre-existing dust-lead hazards. At
the same time, the proposed provision
would not result in the certainty
regarding elimination of dust-lead
hazards that is the defining
characteristic of a clearance
requirement. In addition, the practical
effect of such a provision is that the
proposed clearance requirement would,
in fact, often result in a dust wipe
testing requirement. As such, it raises
many of the same issues and concerns
that ultimately persuaded EPA not to
promulgate just dust wipe testing
requirements.
Furthermore, as stated above, EPA
does not believe the record before it
strongly supports the line-drawing in its
2010 proposal, which would have
resulted in a clearance requirement for
some renovations, a dust wipe testing
requirement for others, and no testing
for the rest of the renovations covered
by the RRP rule.
In revising the abatement regulations
to apply to renovations, EPA has sought
to keep the renovation requirements
relatively simple and easy to apply,
while attaining the overall objective of
minimizing exposure to dust-lead
hazards generated by renovation
activities. EPA is concerned that the
proposed three-tier system would add a
level of complexity to the rule that is
undesirable. While EPA could
potentially draw different lines in this
final rule, or promulgate a requirement
that all jobs achieve clearance, EPA does
not believe it has a strong basis to do so.
The combination of these factors has
convinced EPA that imposing a
clearance requirement is unwarranted.
The best evidence that EPA has of the
effectiveness of the work practice
standards is the Dust Study, and it
demonstrates that overall the full suite
of RRP work practices is effective at
minimizing exposure to dust-lead
hazards created by renovations. Without
more, EPA is unable to conclude that
the RRP work practice promulgated in
2008 should be significantly altered.
Additionally, a variety of
commenters, including industry
representatives and some states,
suggested that EPA had issued its 2010
proposal to require dust wipe testing
and clearance too soon after
promulgation of the 2008 RRP rule. At
the time that the 2010 proposal was
issued, full implementation of the 2008
RRP rule had only just begun.
Commenters contended that renovation
firms were still in the process of
working through how to achieve
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compliance with the rule on a daily
basis and that EPA should wait to add
new requirements until firms were
generally comfortable with the
requirements promulgated in 2008.
Commenters also argued that EPA
should not make a determination that
additional requirements are needed
without first carefully assessing the
status and impact of the existing RRP
rule when fully implemented. EPA
agrees with the general principle
expressed by these commenters—that it
is premature to impose significant
additional work practice requirements
for renovations already covered by the
RRP rule, particularly given the
information before the Agency. EPA also
agrees that many renovation firms are
still determining what the RRP rule
requires from them on renovation
projects. EPA also acknowledges that
there are practical implementation
issues with promulgating a significant
change so soon after thousands of
renovators have become certified
renovators, and have taken the required
training, which did not include
information on the proposed dust wipe
testing or clearance requirements.
Some commenters suggested that EPA
concentrate on RRP education and
outreach at this time, rather than on
additional requirements. EPA agrees
that outreach and education on lead
poisoning in general, and the link
between renovations and increased
blood lead levels in particular,
continues to be important. As part of the
RRP program’s Lead-Safe Certified
media campaign, EPA developed and
made available to the public outreach
materials aimed at both contractors and
consumers. The materials include a
Public Service Advertising (PSA)
advertisement aimed at contractors,
banners for Web sites, sample articles
for magazines, newsletters or other
publications to help inform contractors
about the rule, post cards and buck slips
to stuff into mailers, as well as an
informational brochure about the rule
for building managers. EPA has also
developed fact sheets about the RRP
rule that hardware or paint supply
stores can hand out to their customers
to inform them of the regulatory
requirements. All of this information is
available to the public on EPA’s Web
site at https://epa.gov/lead/pubs/lscppress-materials.htm.
The Agency has also developed
outreach materials for consumers in
order to build demand for lead-safe
certified firms among the public. The
consumer outreach materials include
consumer print advertisements, PSA
radio advertisements in English and
Spanish, and a fact sheet about the RRP
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rule that contractors can provide to
consumers to inform them about the
advantages of hiring lead-safe
renovation firms. The consumer
outreach materials are also
downloadable from EPA’s Web site at
https://epa.gov/lead/pubs/lscpconsumers.htm.
Finally, in an effort to raise awareness
of the consequences of lead poisoning
among parents and pregnant women
who live in homes built before 1978, the
Coalition to End Childhood Lead
Poisoning, EPA and HUD joined the Ad
Council in April 2010 to launch a
national multimedia PSA campaign. As
stated in the PSA campaign press
release, the most common pathways for
lead poisoning are deteriorating leadbased paint (on older windows, doors
and trim, or walls) or improperlyperformed renovation, repair and
painting activities that cause paint to
chip, peel, or flake.
EPA will continue to evaluate and
consider additional outreach and
educational opportunities to improve
property owner and occupant
understanding of dust-lead hazards
created by renovations. EPA also will
continue to monitor implementation of
the RRP rule. If future information,
studies, or data indicate that the existing
RRP rule work practices are not reliable,
safe, and effective, EPA will consider
whether additional requirements should
be proposed.
2. Elimination of provision allowing
clearance in lieu of cleaning
verification. In the 2010 proposal, EPA
proposed to eliminate the existing
provision that allows renovation firms
to skip the cleaning verification part of
the mandatory cleaning protocol if
another Federal, State, or local law or
regulation, or the contract between the
renovation firm and the property owner
requires the renovation firm to use
qualified entities to perform dust wipe
testing and requires the renovation firm
to achieve clearance. The rationale for
eliminating this provision was based on
the fact that, as discussed in the
preamble to the 2010 proposal and the
preamble to the 2008 RRP final rule,
cleaning verification is an integral part
of the whole suite of RRP work
practices. The Dust Study demonstrates
that these practices, when observed as a
whole, are effective at minimizing
exposure to dust-lead hazards generated
by renovations.
EPA received only a handful of
comments on this aspect of the 2010
proposal. Commenters thought that
removing this provision from the RRP
rule would make the rule inconsistent
with the HUD regulations or State or
local laws. Some believed that requiring
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both cleaning verification and clearance
was unnecessarily burdensome, and
pointed out that persons trained in leadsafe work practices had been achieving
clearance without cleaning verification
for a number of years now. While EPA
does not agree with all of these
assertions, EPA does agree that it is
unnecessary to require renovation firms
who must achieve clearance to follow
the specific cleaning verification
protocol. After all, these firms must
continue to clean until they achieve the
clearance standards. As discussed in the
preamble to the 2010 Proposal, and
mentioned by some commenters
specifically in reference to this
provision, contractors who receive the
regular feedback provided by a
clearance requirement have learned how
to clean so that they typically achieve
clearance on the first attempt.
Specifically, in its Evaluation of the
HUD Lead-Based Paint Hazard Control
Grant Program (Ref. 10), HUD noted that
the rate of passing initial clearance was
associated with repetition of lead hazard
control activities. Therefore, EPA is
retaining the provision that allows the
cleaning verification step to be skipped
if the renovation firm must also achieve
clearance. However, EPA believes that
renovation firms whose projects are
subject to clearance only as a result of
contractual requirements are less likely
to gain the repetitive experience of
cleaning sufficiently so as to meet
clearance with few cleaning cycles, so
EPA encourages property owners who
include clearance in their renovation
contracts to also require renovation
firms to perform cleaning verification.
EPA also notes that States and Tribes
are free to include both clearance and
cleaning verification in their laws and
regulations.
3. Paint chip sample collection. In
May 2010, EPA proposed to give
certified renovators another option for
determining whether lead-based paint is
present on components to be affected by
a renovation. This option would allow
certified renovators to collect paint chip
samples from components to be affected
by a renovation instead of using test kits
to test the paint on the components. The
samples would be required to be sent to
an entity recognized under the NLLAP
for analysis. In issuing this 2010
proposal, EPA reasoned that it would be
easy to teach certified renovators to
collect paint chip samples in the
renovator course and this would
provide maximum flexibility for
certified renovators and renovation
firms.
EPA received a number of comments
on this part of its 2010 proposal. Some
commenters supported this option
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because they felt that it is easy to
properly collect a paint chip sample,
and they agreed that this would provide
additional needed flexibility for
certified renovators and renovation
firms. One commenter stated that, as a
homeowner, he had been instructed by
an NLLAP laboratory over the telephone
on how to properly collect a paint chip
sample and forward it to the laboratory
for analysis. This experience led him to
believe that it would be feasible to
include in the renovator course
instruction on how to collect a paint
chip sample and forward it for analysis.
Other commenters did not support this
aspect of the 2010 proposal because
they believe that only certified
inspectors or risk assessors should be
permitted to collect paint chip samples
or make determinations about the
presence or absence of lead-based paint.
Several noted that this would conflict
with State laws that prohibit anyone
other than a certified inspector or risk
assessor from sampling for lead-based
paint. Some commenters expressed
concern about the length of the
renovator course, and the ability to add
the additional information on paint chip
collection, including information on
chain-of-custody issues and laboratory
submission procedures, without
lengthening the course beyond 8 hours.
Others noted that renovators are already
being taught many of the necessary
skills during instruction on how to
properly use test kits.
Because renovator training courses are
already required to include training in
how and where to use test kits, and the
associated recordkeeping requirements,
EPA agrees with those commenters who
believed that it would take very little
additional time to also provide
renovators with specific training in how
to collect a chip sample and submit it
for analysis. The selection of locations
to test and the recordkeeping
requirements would be identical
whether test kits or paint chip sampling
is used, except that the laboratory report
would also have to be maintained along
with the records associated with the
renovation. EPA also agrees with those
commenters who thought that this
option would provide additional
important flexibility. EPA is
promulgating the proposed option
allowing certified renovators to collect
paint chip samples from painted
components that will be disturbed by a
renovation and submit those samples to
an NLLAP-recognized entity for
analysis. EPA will modify the model
certified renovator training course to
add the necessary information on
sample collection, chain-of-custody, and
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laboratory submission procedures. One
commenter wondered how renovators
who have already taken the training to
become certified would learn about this
option and how to use it. EPA will post
the information developed for the
renovator training course on its Web
site. EPA will also e-mail this
information to certified renovation firms
that provided an e-mail address on their
certification applications. As pointed
out by several commenters, paint chip
sample collection, by itself, is a
relatively simple thing to learn and EPA
believes that certified renovators who
have already been trained in how to
properly use a test kit will be able to
learn how to properly collect a paint
chip sample and submit it to an NLLAPrecognized entity from the material EPA
posts on its Web site.
At least one commenter pointed out
that EPA would also have to modify the
recordkeeping requirements to
accommodate this option and include
information specific to paint chip
sample collection, such as component
and location tested, identity of the
NLLAP entity analyzing the samples,
and the sample results. Accordingly,
EPA is modifying 40 CFR 745.86(b)(1) to
add a new subparagraph (iii) that
requires records pertaining to paint chip
sample collection and analysis,
including a description of the
components that were sampled, and the
locations sampled, the name and
address of the NLLAP-recognized entity
performing the analysis, and the results
for each sample. EPA is also modifying
40 CFR 745.86(b)(6) to include a
certification by the certified renovator
that, if paint chip samples were
collected, that the samples were
collected from the components in the
locations specified, that the samples
were submitted for analysis to the
identified NLLAP-recognized entity,
and that the sample results were as
specified.
This option does not make certified
renovator the equivalent of a certified
lead-based paint inspector. Certified
renovators must still test each affected
component, they are not permitted to
exclude components based on similar
painting histories or perform random
paint sampling in multi-unit buildings.
Just as with the current provisions for
test kit use, in those states that do not
permit persons other than certified
inspectors or risk assessors to sample or
test for lead-based paint, certified
renovators will not be able to exercise
this option.
4. Training provider accreditation. In
May 2010, EPA proposed a number of
minor changes to the training provider
accreditation provisions. EPA received
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very little public comment on these
proposed amendments, and EPA is
promulgating these amendments as
proposed.
a. Documentation of personnel
qualifications. The first of these minor
amendments involves submission of
documentation of training program
manager and principal instructor
qualifications along with training
provider applications for accreditation.
Training providers who wish to provide
renovator, dust sampling technician, or
lead-based paint activities training for
Federal certification purposes must
apply for and receive accreditation from
EPA. To become accredited, a provider
must employ a training program
manager as well as principal
instructor(s) who meet certain
education, training and work experience
requirements. The training provider
must indicate on its application for
accreditation that the training program
manager and principal instructor(s)
meet these requirements; however, the
2008 RRP rule did not require
documentation (e.g., resumes) regarding
the qualifications of these individuals to
be submitted to EPA. The Agency
believes it is important to review this
information when determining whether
to approve a training provider
application. When EPA reviews
applications for accreditation, it is
common for the Agency to request this
documentation from training providers
in order to verify that the training
program manager and principal
instructor(s) have the proper
qualifications. Requesting this
information takes time and can delay
the review of an application. Therefore,
the Agency will now require training
providers to submit documentation
regarding the qualifications of the
education, training and work experience
of training managers and principal
instructors with their applications for
accreditation. Only one commenter
commented on this provision,
expressing general support for the
change.
b. Submission of training course
materials. EPA is also promulgating
other proposed changes to the required
materials that must be submitted along
with an accreditation application. EPA
received only one comment expressing
general support for this proposed
change. Specifically, to become
accredited, a training provider must
submit a copy of its training course
materials with its application for
accreditation for review by the Agency.
If a training provider chooses to use the
model course developed by EPA or a
course approved by an authorized State
or Indian Tribe, then the provider is not
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currently required to submit the course
materials with its application. Instead,
the training provider indicates on its
application that it will use the EPA
model course or a course approved by
an authorized State or Indian Tribe.
Authorized States and Indian Tribes can
have renovation or abatement programs
that are significantly different from the
EPA-administered program which
would be reflected in their approved
course materials. In these instances, a
training course approved by the State or
Indian Tribe may not be sufficient for
the purposes of training someone on the
requirements of the Federal program.
Accordingly, the Agency proposed to
require training providers who apply to
EPA for accreditation and wish to use a
course approved by an authorized State
or Indian Tribe to submit the course
materials for EPA review. EPA reasoned
that this will give the Agency the
opportunity to identify and address any
significant differences between the
requirements of EPA and the authorized
program that may appear in the course
so the Agency can ensure that EPAaccredited training providers are using
appropriate course materials.
EPA is promulgating this provision as
proposed. This provision only applies to
those training providers who wish to
use a training course approved by an
authorized State or Indian Tribe that is
different from the EPA model training
course. Training providers wishing to
use the EPA model courses need not
submit those materials with their
applications.
c. Role of principal instructor. EPA is
promulgating a proposed minor
amendment involving a clarification of
the role of principal instructors in
teaching courses. The regulation, at 40
CFR 745.225(c)(3), states that principal
instructors are responsible for the
organization of their courses and
oversight of the teaching of all course
material. The regulations also define
‘‘principal instructor’’ as ‘‘the
individual who has the primary
responsibility for organizing and
teaching a particular course.’’
Nonetheless, the rule also allows
training program managers to designate
experts in a particular field (e.g., doctors
or lawyers) as guest instructors, on an as
needed basis, to teach discrete portions
of the course. EPA interprets these
provisions to require a principal
instructor to be present and primarily
responsible for teaching the course,
although guest instructors may be used
to teach some portion(s) of the course.
Principal instructors are also
responsible for the quality of the
instruction delivered by the guest
instructors. To ensure that the
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regulation is clear on this point, EPA
proposed to amend 40 CFR
745.225(c)(3) to state that principal
instructor(s) are primarily responsible
for teaching the course materials and
must be present to provide instruction
(or oversight of portions of the course
taught by guest instructors) for the
course for which he has been designated
the principal instructor. EPA received
two comments on this provision, both
supported the change, and one
specifically stated a belief that having
principal instructors present while guest
lecturers teach would improve the
content of many courses. EPA agrees
with these commenters and EPA is
promulgating this provision as
proposed.
d. Application amendments. EPA is
promulgating as proposed another
minor amendment involving a specific
provision requiring training providers to
amend their accreditation application
whenever there is a change to the
information presented in their most
recent accreditation or re-accreditation
application. The RRP rule includes
requirements for amending the
certification of a renovation firm. Firms
must submit an amendment within 90
days of the date that a change occurs to
information in its most recent
application for certification or recertification. Examples of amendments
include a change in the firm’s name
without transfer of ownership, or a
change of address or other contact
information. To amend its certification,
a firm must submit an application,
noting on the form that it was submitted
as an amendment. The firm must
complete the sections of the application
pertaining to the new information, and
sign and date the form. EPA has
interpreted the training provider
accreditation regulations to require
accredited training providers to submit
amended applications whenever there is
a change to the information provided in
the training provider’s most recent
application for accreditation or reaccreditation, including information
regarding the training manager and any
principal instructor(s) teaching courses
offered by the training provider.
However, the existing regulations do not
specify a time limit for submitting an
amendment, so EPA proposed to require
training providers to submit
amendments within 90 days of the date
a change occurs to information in each
provider’s most recent application. As
proposed, if the training provider does
not amend its most recent accreditation
application within the 90-day time
period, it must stop providing training
until the accreditation application is
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amended. EPA also proposed to approve
or disapprove amendments for a new
training manager, any new or additional
principal instructors, or any new
permanent training location within 30
days of the date EPA receives the
amendment. This 30-day time period
will give EPA time to check the
qualifications of the training manager(s)
or principal instructor(s) before the
training manager begins managing or the
principal instructor begins teaching a
course. This 30-day time period also
gives EPA time to verify the suitability
of a new permanent training location by
visiting the location. As proposed, the
training provider would not be
permitted to provide training under the
new training manager or offer courses
taught by any new principal
instructor(s) or at the new training
location until EPA either approves the
amendment or 30 days has passed. EPA
also proposed to clarify that no fee will
be charged for accreditation application
or certification amendments. EPA
received no comments on this proposed
amendment.
Because qualified training managers
and principal instructors are critical to
ensuring effective training, it is
important for EPA to have the ability to
review their qualifications before they
begin to provide training. If unqualified
individuals provide training, it could be
very difficult to determine whether the
trainees received adequate training and
resolve any concerns over the quality of
the training. Requiring retraining would
not only inconvenience the training
provider, it would also be burdensome
for the trainees themselves. Therefore,
EPA is promulgating the 30-day review
period for new training managers and
principal instructors as proposed, with
several modifications. The first relates
to the calculation of the 30-day review
period. EPA is clarifying that the 30-day
period begins upon submission of a
complete application for amendment.
Thus, if the amendment involves a new
training manager or principal instructor,
the training provider must fill out the
section of the application that identifies
the training provider and the sections
that pertain to the new training manager
or principal instructor, sign the
application, and include the
individual’s qualifications along with
the application for amendment. If the
application does not include these
items, then the 30-day review period
would not begin until the missing
information is submitted.
In addition, in further reviewing this
proposed provision, EPA has decided
that additional flexibility would be
beneficial for training providers. If the
training provider wishes to use a
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training manager or principal instructor
who has already been reviewed by EPA
as part of a successful application for
training provider accreditation under 40
CFR 745.225, whether for that training
provider or another, the training
provider may do so on an interim basis
without delay. The training manager or
principal instructor must still meet the
qualifications for the position as
described in 40 CFR 745.225(c)(1)–(2).
If, within 30 days of the date that the
training provider begins using such an
individual as a new training manager or
principal instructor, EPA determines
that the individual should not be used
in such a capacity, EPA will provide
written notice to the training provider.
The training provider must stop
providing training under the new
training manager or principal instructor
upon receipt of written notice from
EPA.
With respect to new permanent
training locations, EPA is also
concerned that a poor choice of location
could negatively affect the quality of
training. For example, if a location is
chosen that does not have a suitable
surface for performing cleaning
verification, trainees would be unable to
experience actually doing, during the
hands-on portion of the course,
something that will be an important part
of their responsibilities as certified
renovators. However, EPA believes that
the choice of training location does not,
in most cases, have as big of an impact
on the quality of training as the training
manager or the principal instructor.
During the accreditation process for new
training providers, it has been EPA’s
practice to review the qualifications for
each and every training manager and
principal instructor named on an
application. In contrast, where a
training provider has identified multiple
permanent training locations in its
application, EPA has chosen to visit a
sample of locations, rather than each
and every location. In addition, EPA has
been approving traveling training
providers based on the criteria that the
providers will use to select a training
location, a demonstration of the handson training, and an examination of the
equipment the providers plan to use in
training. Therefore, EPA will allow
training providers to use new
permanent training locations on an
interim basis for 30 days. If, during that
30 days, EPA determines that the
location is not adequate, the training
provider must stop using that location
upon written notice from EPA.
e. Hands-on training requirements.
Another minor amendment involves the
topics for which hands-on training is
required in the renovator and dust
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sampling technician courses. The
regulations at 40 CFR 745.225 includes
requirements and procedures that
training programs must follow to
become accredited in order to provide
instruction in lead-based paint courses.
Minimum requirements for training
curricula are found in this section,
which lists course topics that must be
included in the different training
courses with an indication of the topics
that require hands-on instruction.
However, EPA inadvertently omitted
indicating which course topics required
hands-on training for the renovator and
dust sampling technician disciplines.
Accordingly, EPA proposed to identify
in 40 CFR 745.225(d) which topics in
the renovator and dust sampling
technician courses require hands-on
training. In further clarification, EPA
also proposed to add a sentence to 40
CFR 745.225(e)(2) stating that refresher
courses for all disciplines except project
designer must include a hands-on
component.
EPA received several comments on
this aspect of the 2010 proposal. Two
commenters supported the proposed
topics for hands-on training for
renovators and dust sampling
technicians. Another commenter
wondered why report preparation
would be a required hands-on topic for
dust sampling technicians when it has
never been a hands-on topic for the
other disciplines that must prepare
reports. While it is true that hands-on
training in report preparation is not
required for most lead training
disciplines, it is required for the
inspector discipline. Thus, certified
inspectors and certified risk assessors,
who must successfully complete both
the inspector course and the risk
assessor course, receive hands-on
training in report preparation. EPA
believes that report preparation for dust
sampling technicians is likewise
important enough to warrant hands-on
training in how to do it properly.
Accordingly, EPA is finalizing the
required hands-on training topics as
proposed. Renovator trainees must
receive hands-on training in using test
kits, renovation methods that minimize
creation of dust and lead-based paint
hazards, containment and cleanup
methods, and cleaning verification. Dust
sampling technician trainees must
receive hands-on training in dust
sampling methodologies and report
preparation.
EPA received two comments
specifically on the proposed addition of
a statement that all refresher training
courses, with the exception of the
project designer refresher course, must
include hands-on training. One
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commenter was an environmental
advocacy group, the other an industry
trade association. Neither commenter
supported this aspect of the 2010
proposal; they thought that requiring
hands-on training for renovator
refresher courses would limit the
availability of refresher training and
increase costs unnecessarily. Both
commenters thought that enough
information could probably be conveyed
in a distance learning or e-learning
setting to warrant dispensing with the
hands-on requirement for renovator
courses. The environmental advocacy
group pointed out that EPA’s current
model refresher training course for
renovators contains two required handson skill sets—test kit usage and cleaning
verification. This commenter felt that
this was appropriate, given that
previously-trained individuals are still
taking advantage of the
‘‘grandfathering’’ provision that allows
them to successfully complete an
accredited renovator refresher course to
become certified renovators. Those
individuals would not have had
previous training in those two skills, so
hands-on training would be necessary.
However, once the grandfathering
provision is no longer available, as
discussed later in this section of the
preamble, all certified renovators would
have had hands-on training in these
skills. While EPA agrees with this
commenter that, for now, it is
particularly important for renovator
refresher courses to include hands-on
training in test kit use and in cleaning
verification, EPA disagrees that handson refresher training is unnecessary. A
hands-on component for refresher
courses will help ensure that certified
renovators remain competent in the
skills needed to comply with the RRP
rule, including test kit use, containment,
and cleaning (including cleaning
verification). Therefore, EPA is
finalizing the proposed amendment to
40 CFR 745.225(e)(2) that specifically
states that hands-on training is required
for all refresher courses except project
designer. EPA plans to re-evaluate the
renovator refresher course after the
grandfathering provision sunsets, but
before the currently-certified renovators
are due for refresher training. At that
time, EPA will consider whether handson training is still necessary and
appropriate for renovator refresher
training.
f. E-learning. As stated in the 2010
proposal, Web-based training and other
types of alternative training delivery are
permitted under both the Lead-based
Paint Activities Regulations and the
RRP rule. An EPA model on-line
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renovator course that may be used to
deliver the classroom portion of the
renovator course is available. While
such alternative training delivery
options cannot be used to deliver
required hands-on training, EPA
encourages training providers to make
use of such options where appropriate
to increase access to training and make
it more affordable. Web-based training
courses are considered separate courses
and a separate application fee is
required for each.
EPA’s model electronic training
course contains certain basic
administration and delivery
requirements. These include assigning a
unique identifier to each student, to
allow the training provider to track
student course progress and completion.
In addition, there are knowledge checks
for each chapter, which must be
completed before the student can go on
to the next chapter, and a final test for
the electronic learning portion which
consists of at least 20 questions. Finally,
students must be able to save or print
an uneditable copy of a record showing
completion of the electronic learning
portion of the course. In May 2010, EPA
proposed to incorporate these
requirements into 40 CFR 745.225 to
ensure that all training providers
wishing to use electronic learning for
the classroom portions of lead-based
paint courses are aware of these
requirements and plan their course
development accordingly. EPA
requested comment on a variety of
topics, including the number of
questions in the course test and the
score required to pass.
EPA received several comments on
this aspect of the 2010 proposal. Some
commenters were concerned with
verifying the identity of persons logging
into e-learning courses. Several noted
that, because it is impossible to verify
with certainty the identity of persons
completing online training, an in-person
final course test is necessary to ensure
that the trainee is adequately trained. In
this final rule, EPA is amending 40 CFR
745.225(c)(6) to explicitly require
e-learning training providers to assign a
unique identifier to each student in
order to track the student’s progress
through the course. EPA believes that
this requirement, along with the existing
requirement that the trainee participate
in the hands-on training and take the
final course test in person, will provide
reasonable assurance that the same
person has completed all of the portions
of the course. In response to these
commenters, EPA is modifying the
regulations to specifically state that
e-learning or other alternative delivery
methods cannot be used for the hands-
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on training, the final course test, or the
proficiency test, if one is given.
Commenters also expressed concern
that the EPA model online course could
be completed in as little as one hour,
which could mean that a person could
become a certified renovator with only
3 hours of training. EPA disagrees with
these commenters. The current model
course posted on the EPA Web site is
not a functioning course and does not
contain the background learning
management system (LMS) which tracks
the student’s progress and requires
satisfactory completion of the
knowledge checks and the final test.
Therefore, the time it takes to page
through the model course is not
representative of the time it would take
to successfully complete an accredited
e-learning course. Assuming that 2
training hours are spent on hands-on
training, 40 CFR 745.225(c)(6)(vi)
requires a minimum of six 50 minute
training hours or 5 hours of classroom
time for renovators. This requirement
applies equally to traditional classroom
settings as well as to e-learning courses
offered for accreditation. While EPA
realizes that renovator trainees will not
all proceed through an e-learning course
at the same pace, an e-learning course
offered for accreditation must be
generally designed so that an average
trainee takes approximately 5 hours to
proceed through the course, including
all of the knowledge checks and the
course test.
One commenter thought that EPA’s
proposed requirement of an 80%
minimum passing score on the course
test for the online course was too
restrictive. Another commenter
disagreed, reasoning that an 80%
minimum passing score was reasonable
but that a 100% passing score would be
too restrictive, because it would likely
result in students being penalized for
poorly-worded questions or alternate
interpretations, regardless of the state of
the student’s knowledge. This
commenter thought that it was
appropriate to have a higher passing
score requirement for the e-learning
portion of a training course, because the
student would have an opportunity to
review the material and retake the test.
EPA agrees with the second commenter.
The 80% minimum passing score is
intended to demonstrate mastery of the
subject and lower scores do not achieve
this goal. If students do not pass the test,
they must review the material and try
again. To ensure that, just as in
conventional testing, students using
electronic means to take the test do not
receive feedback on their answers until
after they complete and submit the test,
the electronic testing provision at 40
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CFR 745.225(c)(6)(viii)(D) explicitly
prohibits such interim feedback, a
feature contained in some Web sites.
One commenter suggested that EPA
consider separately accrediting entities
that provide online training and entities
that provide hands-on training. The
commenter argued that developing an
online course is a capital-intensive
project that requires a large number of
trainees to recover the costs, so
relatively few entities are likely to
undertake online course development.
In contrast, the commenter stated that
the delivery of hands-on training must
be more local and mobile, it requires a
smaller capital investment, and each
entity may have relatively few trainees.
EPA recognizes that this may be the
case, at least for now, while EPA is
administering the RRP program in most
States. However, this may change as
more States become authorized and
impose requirements for training that
may differ from the EPA requirements.
In any event, as the commenter notes,
EPA has developed a streamlined
process to allow accredited training
providers to add an e-learning
component to their accreditation by
using an already developed and
accredited online course. This allows
accredited training providers to offer
online training without having to make
a large capital outlay to develop a
course. EPA continues to believe that
the training provider who issues the
final course completion certificate to a
trainee, thus conferring certified
renovator status on the trainee, must be
responsible for ensuring that the student
has completed all of the required
training. EPA does not offer partial
accreditations, or accreditation for a
portion of a course.
On a related topic, this commenter
thought that it would be burdensome to
require the hands-on training provider
to maintain records of the specific times
each student logged in to the online
portion of the course, each student’s
progress, and completion data. The
commenter believed that, in the case
where the online provider and the
hands-on provider are separate entities,
working under a contractual agreement
to present an entire training course, it
would be relatively easy for the online
provider to maintain the records. In
contrast, the commenter thought that it
would be much more burdensome for
EPA to require that the hands-on
provider download or otherwise take
possession of these records. EPA
disagrees with this commenter, because
EPA believes that the amount of data
associated with this particular
requirement for each trainee is not
substantial. However, if a particular
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accredited training provider felt
otherwise, the provider could contract
with the provider of the online training
to store the records. Although the
accredited training provider would
remain ultimately responsible for being
able to produce those records, as long as
the training provider is able to produce
them in response to a request from EPA,
EPA would consider the training
provider in compliance with the
recordkeeping requirements.
One commenter provided a number of
specific comments on EPA’s proposed
requirements for e-learning courses.
First, the commenter thought that the
requirement for knowledge checks for
each module of the course was too
inflexible, and that it could be difficult
to determine what a module is for
purposes of knowledge checks. The
commenter suggested that EPA instead
require periodic knowledge checks. EPA
agrees with this comment and is
promulgating a requirement for periodic
knowledge checks equivalent to the
number and content of the knowledge
checks contained in EPA’s model
course. This would be 16–24 knowledge
checks over the entire course. This
commenter also thought that the
requirement that a student be able to
generate an uneditable copy of an elearning course completion certificate
too stringent. The commenter pointed
out that almost anyone reasonably
familiar with computers could alter a
secure PDF, image, or word processing
file through the print function. EPA will
add language to the proposed provision
at 40 CFR 745.225(c)(6)(viii)(E) to clarify
that EPA merely meant that the
certificate must not be susceptible to
easy editing. A secure PDF file would
comply with these requirements.
Allowing students to generate and print
the course completion certificate
provides them with reasonable certainty
that they have completed the e-learning
portion of the course before attempting
the hands-on portion. EPA recommends
that accredited training providers verify
through other means, such as the elearning progress records, that each
student who completes the hands-on
training has also completed the online
portion of the course before training
providers issue the final course
completion certificate.
g. Combined refresher courses. In the
2010 proposal, EPA requested comment
on whether training providers should be
allowed to provide a combined
Abatement Worker/Renovator refresher
course or a combined Abatement
Supervisor/Renovator refresher course
or both. After the 2008 RRP rule was
promulgated, EPA received input from
the regulated community and others
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indicating that many abatement
contractors are likely to also become
certified renovation firms. If this is the
case, it would be advantageous for such
firms to be able to send their employees
to combined refreshers so that the
employees would more readily be able
to keep up their dual certifications. EPA
requested comment on the likelihood
that this will be the case, and, if
combined refreshers are desirable,
whether the different certification time
periods for individual abatement
certification (3 years) and individual
renovator certification (5 years) should
be harmonized and, if so, how. EPA
received two comments on this topic;
both commenters supported the idea of
combined refresher courses and thought
they would provide increased flexibility
for industry. One commenter thought
that the certification time periods
should be harmonized to 3 years for all
disciplines because the commenter
believed that 5 years was too long to go
without a refresher. The other
commenter did not think that
harmonization was necessary, because
the abatement worker or supervisor
would just take the combined refresher
every 3 years to meet the shorter
certification periods in the Lead-based
Paint Activities Rule. EPA agrees with
these commenters that combined
refresher courses may be beneficial.
While the current regulations permit
training providers to offer refresher
courses sequentially, e.g., a 4-hour
renovator course on the afternoon of one
day, followed by an 8-hour worker
course the next day, taking the courses
sequentially would result in some
duplication of training topics for
persons certified as both renovators and
abatement workers. On the other hand,
EPA is not certain that appropriate
refresher topics for both disciplines
could be covered in a single 8-hour day.
EPA plans to evaluate the content of its
supervisor, worker, and renovator
refresher courses to determine what an
appropriate combined course length
might be. Depending on the results of
this evaluation, EPA will consider
amending these regulations to establish
course length requirements for
combined refresher courses.
h. Recordkeeping. Another
amendment proposed in May 2010
involves recordkeeping requirements for
training providers. Previously, training
providers were required to keep training
records for 3 years and 6 months. This
length of time was chosen because of
the length of individual certification
periods for lead-based paint activities,
which can be as long as 3 years and 6
months including interim certification.
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However, the renovator and dust
sampling technician certification
periods are 5 years, with no interim
certification. Therefore, in order to
ensure that the training records from the
previous training course are available
for certified renovators and dust
sampling technicians taking refresher
courses, EPA proposed to increase the
recordkeeping period applicable to
these disciplines to 5 years. EPA
received two comments on this aspect of
the 2010 proposal, both commenters
thought that the recordkeeping
requirements for all disciplines should
be increased to 5 years. These
commenters thought it would be less
confusing for training providers if there
was one period applicable to all. One
commenter pointed out that EPA had
extended the certification period for
renovators trained before April 22, 2010
to July 1, 2015, so the training records
for those trainees ought to be kept for as
long as their certification lasts. This
commenter suggested that EPA require
training records to be kept for 5 years or
until the expiration of certification
resulting from the training, whichever is
longer. While EPA agrees that it may be
easier for training providers to keep
records for the same length of time
regardless of the discipline, EPA does
not believe that it is necessary to make
this a requirement. Training providers
who prefer to have one single
recordkeeping process can always
choose to maintain their records for
5 years across the board. Therefore, EPA
is promulgating the increased
recordkeeping requirement for providers
of accredited renovator and dust
sampling technician training as
proposed. EPA also agrees with the
commenter who suggested that there be
a longer recordkeeping requirement for
renovator training courses offered before
April 22, 2010. Accordingly, EPA is also
promulgating a requirement that records
for renovator training courses completed
before April 22, 2010 must be kept until
July 1, 2015.
i. Trainee photographs. EPA also
proposed certain minimum standards
for the trainee photographs that must
appear on renovator and dust sampling
technician course completion
certificates. Accredited training
programs are required to issue a course
completion certificate for each person
who passes a training course. A variety
of information is required to be on the
certificate including the name of the
course, the name and address of the
student, and contact information for the
training program. Course certificates for
renovators or dust sampling technicians
must include a photograph of the
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student, but the regulation does not
include size requirements or other
specifications for the photograph. Since
publishing the 2008 RRP rule, the
Agency has been asked if there is a
minimum size for the photograph. EPA
believes that it would be beneficial to
have minimum standards for the
photograph in order to ensure that the
person in the photograph is
recognizable. EPA proposed to require
that the photographs on course
completion certificates be an accurate
and recognizable image of the trainee
and at least one square inch in size. EPA
also requested comments on whether
the image quality requirements should
be more specific, e.g., more quantitative.
EPA received several comments on this
provision. Commenters generally
supported the proposed requirements,
but did not favor additional
requirements, such as quantitative
requirements for image quality, as they
were concerned about the burden
associated with such additional
requirements. EPA agrees with these
commenters that the proposed
requirements are sufficient. Therefore,
EPA is promulgating the image quality
requirements as proposed.
j. Clarifying changes to 40 CFR
745.225. Finally, as stated previously,
40 CFR 745.225 includes requirements
and procedures that training programs
must follow to become accredited in
order to provide instruction in
renovator, dust sampling technician,
and lead-based paint activities courses.
The final 2008 RRP rule amended
§ 745.225 to cover persons who provide
or wish to provide renovator or dust
sampling technician training for the
purposes of the RRP rule. There are
some instances where the regulations do
not specifically mention the renovator
or dust sampling technician courses
even though the regulations apply to
those courses. For example, 40 CFR
745.225(c)(14) explains the
requirements which a training provider
must follow when submitting
notification to EPA after the completion
of a training. However, the conforming
changes, i.e., to replace ‘‘lead-based
paint activities courses’’ with
‘‘renovator, dust sampling technician,
and lead-based paint activities courses,’’
were not made to every subparagraph
even though all the requirements of that
section apply to those courses.
Consequently, EPA proposed to clarify
that the requirements in 40 CFR 745.225
apply to renovator and dust sampling
technician courses in addition to leadbased paint activities courses. EPA
received one comment offering general
support for these proposed revisions.
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EPA is promulgating these revisions as
proposed.
5. State and Tribal program
authorization. Under the RRP rule,
interested States, Territories, and Indian
Tribes may apply for, and receive
authorization to administer and enforce
all of the elements of the RRP program.
In May 2010, EPA proposed several
changes to the State and Tribal program
authorization regulations. The first was
a clarification that State and Tribal
programs do not need to include
requirements for the accreditation of
dust sampling technicians if they
require dust sampling to be performed
only by a certified inspector or risk
assessor. EPA received only one
comment relating to this proposed
revision, and that commenter thought
that EPA should require States and
Tribes to allow dust sampling
technicians to collect samples.
However, EPA does not have the
authority to prohibit States and Tribes
from having a more stringent program
than the EPA’s, e.g., requiring more
training for persons collecting dust wipe
samples than EPA requires. It would not
make sense for EPA to require States
and Tribes to establish the dust
sampling technician discipline if those
trainees would not be allowed to
perform any duties under State or Tribal
law. Therefore, EPA is promulgating
this change to the text of the regulation
as proposed.
Along these same lines, EPA proposed
to add a provision requiring State or
Tribal programs to have procedures and
requirements for on-the-job training of
renovation workers who do not receive
accredited training. EPA neglected to
include such a provision in the 2008
RRP Rule. As with the dust sampling
technician discipline, State and Tribal
programs are only required to have
these provisions if they permit on-thejob training for renovation workers. If,
for example, a State or Tribal program
only allows certified renovators to
perform renovation activities within a
regulated renovation work area, then no
provisions for on-the-job training would
be required for that State or Tribal
program. EPA received one comment
generally supporting this change. EPA is
promulgating this revision as proposed.
EPA also proposed to amend the State
and Tribal program requirements to
clarify that both individuals and firms
must receive certification. Only one
comment was received on this topic,
pointing out that EPA’s proposed
regulatory text at 40 CFR 745.326(e)(1)
did not accomplish that objective. EPA
agrees with this commenter, and has
revised the regulatory text throughout
this section accordingly to ensure that
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EPA’s requirements are clear. EPA
requires both renovators and renovation
firms to be certified. A renovator
becomes certified by successfully
completing an accredited renovator
training class. A renovation firm
becomes certified by submitting an
application to EPA, attesting that it and
its employees will follow the work
practice standards at 40 CFR 745.85 for
conducting renovations, and paying a
certification fee. EPA believes that, in
order for a State or Tribal program to be
at least as protective as EPA’s program,
the State or Tribal program must, at a
minimum, require formal certification
for renovation firms. States and Tribes
may, but are not required to, formally
certify renovators. The certified
renovation firm is responsible not only
for the behavior of its certified
renovators but also for the other workers
that have been trained by the certified
renovators. Thus, the renovation firm is
ultimately responsible for the proper
performance of the renovation.
Requiring formal certification for
renovation firms facilitates compliance
monitoring and enforcement for EPA as
well as for State and Tribal programs. A
program that only required formal
certification for individual renovators
and not firms would not be as
protective.
In addition, as pointed out by several
State commenters, EPA inadvertently
included the wrong provisions in the
proposed regulatory text for revising
authorized State and Tribal programs to
conform to revisions to the 2008 RRP
rule. The existing provisions at 40 CFR
745.326(f) give authorized State and
Tribal programs 2 years from the
effective date of any EPA revisions to
the 2008 RRP rule to demonstrate that
the State or Tribal program meets the
requirements of the revised 2008 RRP
rule. This 2 year period is also afforded
to States and Tribes that submit
applications for authorization before the
effective date of any EPA revisions. EPA
did not intend to make any changes to
this provision and States and Tribes still
have 2 years to make changes to their
programs necessitated by revisions to
the Federal RRP program.
Finally, EPA proposed to require that,
in order to be authorized for any of the
lead-based paint programs, State or
Tribal programs demonstrate that: (1)
The State or Tribe is able to sue to
obtain penalties, (2) civil and criminal
penalties of at least $10,000 are
assessable for each instance of violation,
(3) if violations are continuous, the
penalties are assessable up to the
maximum amount for each day of
violation, and (4) the burden of proof
and degree of knowledge or intent of the
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respondent is no greater than it is for
EPA under TSCA. EPA also requested
comment on what criteria States or
Tribes should consider in assessing
penalties and whether the $10,000
minimum penalty authority level
should be periodically adjusted for
inflation. As discussed in the preamble
to the proposed rule, in choosing the
proposed minimum penalty authority of
$10,000 per violation per day, EPA
looked to other programs that States and
Tribes may be authorized to administer.
Some of these programs have minimum
penalty authority requirements for State
and Tribal programs and some do not.
For example, under the Clean Air Act
(CAA) implementing regulations at 40
CFR 70.11(a)(3) and the Resource
Conservation and Recovery Act (RCRA)
implementing regulations at 40 CFR
271.16(a)(3), State programs must have
the authority to assess civil and criminal
fines of at least $10,000 per day per
violation. Other programs have
established lower minimum penalty
authority requirements. The
implementing regulations for the Safe
Drinking Water Act (SDWA) require
State programs to have the authority to
impose a penalty of at least $1,000 per
day per violation on public water
systems serving a population of more
than 10,000 individuals. Some EPA
programs have set no minimum penalty
authority requirements for States and
Tribes; these programs include the
Asbestos Hazard Emergency Response
Act program and the State pesticide
applicator certification program under
the Federal Insecticide, Fungicide, and
Rodenticide Act.
EPA received a number of comments
on this provision. Six State commenters
opposed the proposed provisions.
Several argued that their legislatures
had already created the authority to
establish an RRP program, but the
maximum penalty amount was less than
$10,000. Five States described their
existing penalty authorities—one
already has a minimum penalty
authority of $10,000, one has $5,000,
and the other three have $1,000. These
States did not believe that they would
be able to increase the maximum
penalty authority, because it was
comparable to other programs
administered by the State, or that it
would take several years to get an
increase through the legislature, during
which time EPA would have to
administer the program in their
jurisdictions. At least two alreadyauthorized State RRP programs pointed
out that they had been authorized with
maximum penalty authorities of less
than $10,000. One State noted that it
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could assess penalties of up to $750 or
$1,000 under its EPA-authorized RRP
program, the other’s maximum RRP
penalty authority ranged from $1,00 to
$1,000. One of these States also noted
that it had been effectively enforcing the
Lead-based Paint Activities Program and
the Pre-Renovation Education Program
for years now, and the State did not
believe that an increase in its maximum
penalty authority would improve the
effectiveness of its programs in any way.
Another State commented that it has
penalty authority of $10,000, but that
limit is for each enforcement case, not
per violation per day. Some of the State
commenters also noted that most
enforcement actions in an RRP program
would be against very small companies
or individuals, and penalties of less
than $10,000 per violation per day
would still be very effective deterrents
for such entities.
Two environmental advocacy groups
supported EPA’s proposed minimum
penalty authority of $10,000, arguing
that substantial penalties are necessary
to get the attention of the regulated
community and meaningful
enforcement is critical to the rule’s
success at protecting individuals from
exposures to dangerous levels of lead.
EPA agrees with these commenters on
the importance of an effective
enforcement program. Strong
enforcement of the lead-based paint
regulations by authorized State and
Tribal programs is critical to ensuring
the safety of the occupants of target
housing and child occupied facilities
undergoing lead abatement, renovation,
repair or painting. However, EPA also
agrees with those States that argued that
most of the enforcement actions in
authorized lead-based paint programs
would be against very small entities.
Although small entities also violate the
CAA and RCRA, it is likely that the
regulated community in the lead-based
paint programs consists of smaller
entities than the other programs for
which EPA has established minimum
penalty authorities. Therefore, EPA is
establishing a minimum penalty
authority for State and Tribal programs
of $5,000. Because it is especially
important to deter multiple violations
and continuing violations, this final rule
retains the ‘‘per violation, per day’’
requirement.
In response to the related requests for
comment, State commenters did not
favor adding a mechanism for adjusting
these minimum penalty authorities for
inflation. One environmental advocacy
group supported the idea, but thought
that it should not be a barrier to State
and Tribal program authorization. EPA
agrees with these commenters and no
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mechanism for adjusting these
minimums for inflation is included in
this final rule.
Commenters suggested a number of
factors that should be considered by
States and Tribes when imposing
penalties for violations of their
authorized programs. Several favored
enforcement history and risk, but not to
the extent of treating first-time offenders
too lightly. A handful of commenters
argued that size of business, and ability
to stay in business should not be
considered, because small companies
can cause as much harm as large
companies. EPA believes that States and
Tribes may legitimately consider any of
the factors that EPA typically considers,
such as nature, circumstances, and
extent of the violation, the culpability of
the violator, history of prior violations,
ability to pay or continue in business,
voluntary disclosure, and attitude of the
violator. However, EPA will not require
States and Tribes to consider any of
these factors.
Finally, EPA received no comments
on the proposed addition of an explicit
requirement that States and Tribes have
the ability to sue violators to collect
penalties and that the burden of proof
for enforcement be no more rigorous
than the EPA standard under TSCA.
EPA believes that these two elements
are important elements of an effective
enforcement program. Therefore, EPA is
promulgating these additional
requirements as proposed.
6. Vertical containment. EPA’s 2010
proposal included more specific
language on vertical containment
requirements for exterior projects. As
proposed, the rule would specifically
state that vertical containment is
required for exterior renovation projects
that are covered by the rule and that
affect painted surfaces within 10 feet of
the property line. In such cases, vertical
containment is necessary to ensure that
adjacent buildings or properties are not
contaminated by leaded dust or debris
generated by the renovation. EPA’s Dust
Study demonstrates that leaded dust
and debris from exterior renovations can
be found 10 feet away from activities
disturbing leaded paint, even if no
prohibited or restricted practices are
used. For example, in an experiment
involving the dry scraping of paint from
a single story garage, significant dustlead levels were detected on collection
trays at distances from 9 to 11 feet from
the scraping activity (Ref. 6, page 6–25).
These levels ranged from 7,500 μg/ft2 to
more than 16,500 μg/ft2. The RRP rule,
at 40 CFR 745.85(a)(2), requires
renovation firms to isolate the work area
so that no dust or debris leaves the work
area while the renovation is being
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performed. The rule further states, at 40
CFR 745.85(a)(2)(ii)(D), that, in certain
situations, the renovation firm must take
extra precautions in containing the work
area to ensure that dust and debris from
the renovation does not migrate to
adjacent properties. EPA knows of no
work practice other than a system of
vertical containment or equivalent extra
precautions in containing the work area
that would universally and effectively
prevent the migration of dust and debris
from renovations performed within 10
feet of the property line to adjacent
properties.
EPA also proposed to clarify, in the
regulatory text itself, that windy
conditions may also necessitate the use
of vertical containment to prevent
contamination of other buildings, other
areas of the property, or adjacent
buildings or properties. Specific
mention of windy conditions was made
in the preamble to the final 2008 RRP
rule, although it was not included in the
regulatory text. Nevertheless, EPA
expects atmospheric conditions to be
one of several factors that renovation
firms consider when designing
containment systems. Other factors
would include the height of the building
and the paint disturbance and the type
of renovation activity planned. EPA
thought that specifically including
windy conditions as a factor to consider
when designing an effective
containment system would serve as an
important reminder for renovation
firms. Including the mention of windy
conditions in the proposed regulatory
text did not mean that vertical
containment would be required for any
particular renovations. The 2010
proposal also included a definition of
the term ‘‘containment’’ in order to
clarify what is meant by the term. The
proposed definition was based on the
definition of ‘‘Worksite preparation
level’’ from the Department of Housing
and Urban Development’s ‘‘Guidelines
for the Evaluation and Control of LeadBased Paint Hazards in Housing’’ (HUD
Guidelines, Ref. 11). The proposed
definition included additional
information on what constitutes vertical
containment.
Some commenters supported the
proposed revisions to the vertical
containment requirements. One thought
that contamination of neighboring
properties is a common and serious
problem. Other commenters did not
support the proposed revisions. These
commenters thought that the proposed
revisions were too inflexible and
unnecessary. EPA disagrees with these
commenters. As discussed, the Dust
Study shows that dust and debris from
exterior renovations travels at least 10
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feet from the activity. The RRP rule
requires the ground to be covered with
plastic sheeting or other impermeable
material extending 10 feet beyond the
surfaces being renovated or a sufficient
distance to collect falling paint debris,
whichever is greater, unless prevented
by the property line. In the absence of
a system of vertical containment or
equivalent extra precautions in
containing the work area, EPA knows of
no work practice that would universally
and effectively ensure that adjacent
properties are not contaminated when
work disturbs lead-based paint within
10 feet of the property line. One
commenter thought that it should be
sufficient to require the renovation firm
to inform the neighbors to keep their
windows and doors closed while the
renovation is ongoing. While this might
prevent leaded dust from drifting into
the interiors of adjacent buildings, it
does not address contamination of the
neighboring porches, balconies, or
yards. This does not meet the standard
already present in the RRP rule, that
dust and debris not be permitted to
leave the work area while the
renovation is ongoing. EPA is also
concerned about the ability of
renovation firms to affect the behavior
of neighbors whose homes are not being
renovated.
Several commenters expressed
concern about the safety of workers and
vertical containment. One argued that
OSHA has said that vertical
containment is not required in
situations where worker safety would be
compromised, such as in windy
conditions. EPA agrees that erecting
extensive scaffolding to support a large
vertical containment system in some
windy conditions may be unsafe for
workers. If such a vertical containment
system would be necessary to ensure
containment of the dust generated by a
particular renovation, EPA knows of no
alternative but to reschedule the
renovation for a more clement day. The
HUD Guidelines state that exterior
renovation work should not be
conducted when the wind speed is
greater than 20 miles per hour (Ref. 11).
The Guidelines also state that work
must cease and cleanup be completed
before rain begins. EPA has not imposed
these specific requirements, but
renovation firms should consider this
guidance when deciding how to
proceed.
Other commenters were concerned
about the additional costs that the
revisions to the vertical containment
provisions would impose on
renovations and the potential negative
impact on affordable housing and
weatherization programs. EPA agrees
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that it is more expensive to conduct
exterior renovations with vertical
containment than without. In EPA’s
economic analysis for the 2008 RRP
rule, EPA addressed those situations
where the renovation firm must take
extra precautions to effectively contain
dust and debris, including work areas in
close proximity to other buildings, work
areas that abut a property line, and
windy conditions. The 2008 economic
analysis specifically notes that it is
sometimes necessary to erect a system of
vertical containment to prevent paint
dust and debris from contaminating the
ground or any object beyond the work
area. To account for these situations,
EPA estimated that approximately 2%
of exterior jobs would use exterior
containment, and the incremental cost
of vertical containment varies from $330
per wall to $1,640 per wall, depending
on the size of the job. Thus, EPA has
already accounted for the additional
costs incurred for using vertical
containment systems on renovations
performed within 10 feet of the property
line.
Because EPA does not know of any
effective alternatives to the vertical
containment requirement for exterior
renovations performed within 10 feet of
the property line, EPA is promulgating
a requirement that vertical containment
or equivalent extra precautions in
containing the work area be used on
exterior renovations performed within
10 feet of the property line. This
requirement is intended to provide
flexibility for certified renovators to
design effective containment systems
based on the renovation activity and the
work site. To ensure that renovation
firms understand that the requirement
refers to a wide variety of effective work
area containment systems, EPA is
including the phrase ‘‘or equivalent
extra precautions in containing the work
area’’ in this requirement. Effective
work area containment can span a range
from simple barriers to more extensive
scaffolding, depending on the size of the
job and other relevant factors. Complex
vertical containment systems with
extensive scaffolding are often not
necessary to effectively contain the dust
generated by a renovation. An example
of a simple barrier system, on a job
requiring hand scraping within a few
feet of the ground and within a few feet
of the property line, would be laying
plastic or other impermeable material
on the ground between the paintdisturbing activity and the property
line, anchoring it to the house, and then
extending the material up and over the
fence at the property line. A slightly
more extensive containment approach
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could involve the use of a triangular
eave/soffit ‘‘lean-to’’ system. In this
system, plastic or other impermeable
material could be spread out on the
ground 5–10 feet out from the exterior
side wall, depending upon the available
space. The same impermeable material
could be attached to the eave or soffit
area at the roofline, and held away from
the building by an extension ladder
temporarily fastened to where the wall
meets the eave or soffit. The material
would then be fastened and sealed onto
the ground cover. A variation of this
system would involve draping the
plastic or impermeable material over a
frame consisting of commerciallyavailable tension rods or strong painter’s
extension tubes. Effective containment
could also consist of plastic or other
impermeable material draped from
outriggers, or framework secured to the
roofline, taped to the sides of the
building to surround the work area, and
fastened and sealed to the ground cover.
Yet another containment system could
involve a rigid box-like framework,
constructed out of commerciallyavailable tension rods or painter’s
extension tubes, wrapped in
impermeable sheeting and anchored to
the ground cover and the sides of the
building. EPA believes that these
measures, in most cases, should be
sufficient to contain dust and debris
where extra containment measures are
needed, such as work that creates large
amounts of dust or work performed
within 10 feet of the property line.
EPA realizes that it may be costly or
impracticable to deploy an elaborate
vertical containment system, for
example, in high rise multi-story
buildings. The Agency, furthermore
does not wish to create hazardous
situations for workers that would
outweigh the benefit of capturing the
dust with scaffolding-based vertical
containment systems. EPA believes that
equally effective systems may exist.
Thus, EPA added language indicating
that ‘‘equivalent extra precautions in
containing the work area’’ will also
satisfy the requirement to contain dust
on the worksite of exterior renovations
performed within 10 feet of the property
line.
EPA continues to believe that it is
important to remind renovation firms
that there may be other situations where
vertical containment or equivalent extra
precautions in containing the work area
would be required in order to prevent
dust and debris from leaving the work
area. However, because some
commenters appeared to believe that
EPA’s mention of windy conditions
amounted to a requirement to use
vertical containment in windy
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conditions, EPA is deleting the phrase
‘‘such as in windy conditions.’’ The
complete provision, as promulgated,
reads: ‘‘If the renovation will affect
surfaces within 10 feet of the property
line, the renovation firm must erect
vertical containment or equivalent extra
precautions in containing the work area
to ensure that dust and debris from the
renovation does not contaminate
adjacent buildings or migrate to adjacent
properties. Vertical containment or
equivalent extra precautions in
containing the work area may also be
necessary in other situations in order to
prevent contamination of other
buildings, other areas of the property, or
adjacent buildings or properties.’’ EPA
wishes to encourage innovation in
designing effective containment systems
or measures, so EPA will consider any
information or data made available to it
that could be used to determine the
equivalence of extra containment
precautions in containing the work area.
For example, the Department of Energy
(DOE) suggested that an equivalent
containment system could involve the
use of a trough-like system beneath the
paint-disturbing work. The trough
would consist of polyethylene and
tubing fabricated in a U-shape
configuration, extending 1 to 2 feet from
the exterior side of the building.
According to DOE, the bottom of the
trough could be weighted down with
scrap lumber and sprayed with water
enabling it to capture the falling dust
and debris. DOE suggested that this
trough, especially if combined with dust
minimization techniques such as wet
methods, the use of dust-capturing
shrouds, and HEPA vacuums, would be
equally effective at containing dust and
debris as vertical containment. EPA
cannot determine that the trough, by
itself, provides effective containment of
dust and debris, but will be examining
this in the future. Similarly, DOE
suggested that another possible method
for the dust that is generated during an
exterior renovation to be captured could
involve the use of a shroud attached to
a power tool with a HEPA vacuum, also
attached to the shroud, where the dust
and debris is captured right at the
source—thereby not allowing it to fall
onto polyethylene, workers clothing,
equipment, and tools. EPA seeks data or
other information upon which to
evaluate that the following are effective
at containing dust and debris: the trough
in combination with dust minimization
techniques; the use of a shroud attached
to a power tool with a HEPA vacuum;
or other alternative methods. EPA will
review and issue guidance as
appropriate. EPA intends to work
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collaboratively with DOE and HUD and
other agencies and stakeholders as
appropriate to develop further guidance
on equivalent extra precautions in
containing the work area.
In addition, since promulgation of the
2008 RRP rule, EPA has received several
inquiries from the regulated community
on the rule’s containment provisions. In
particular, EPA has been asked to
address the problem of obstacles that
prevent renovation firms from using 6
feet of plastic sheeting or other
impermeable material on interior floors
or 10 feet of material on the ground.
EPA believes that the proper use of
vertical containment measures may be a
more effective method for containing
the work area than use of traditional
floor or ground containment alone,
especially where obstacles prevent or
make it impractical to install floor or
ground containment to the extent
required by the RRP rule. Therefore,
EPA is amending the containment
provisions for both interior and exterior
renovations to permit renovation firms
to erect vertical containment closer to
the renovation activity than the
minimum floor or ground containment
distance specified in the RRP rule to
give renovation firms more flexibility in
designing effective containment
strategies for particular work sites. For
exterior renovations, this amendment
would allow a renovation firm to
construct vertical containment less than
10 feet from the renovation activity. If
a renovation firm chooses to take
advantage of this provision, the ground
containment may extend less than 10
feet, stopping just outside the edge of
the vertical containment, as long as the
distance is sufficient to contain all dust
and debris during the renovation and
post-renovation cleanup. For example, a
renovation firm erects an exterior
vertical containment system consisting
of a rigid box-like framework wrapped
in impermeable plastic sheeting and
anchored to the ground and home. If
this containment system is erected 5 feet
from the side of the home, and placed
on top of ground containment, such
containment should effectively limit the
travel of dust and debris to the interior
of the enclosure. Under the amended
containment provisions, the renovation
firm would not be required to extend
plastic sheeting or other impermeable
material another 5 feet beyond the
vertical containment system in order to
meet the 10 foot minimum ground
containment requirement promulgated
in the 2008 RRP rule.
EPA is also providing increased
flexibility for renovation firms by
allowing firms the option to use vertical
containment measures in combination
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with reduced floor containment on
interior renovations. However, to
qualify for reduced floor containment
requirements, vertical containment
systems for interior renovations must
consist of impermeable barriers that
extend from the floor to the ceiling and
are tightly sealed at joints with the floor,
ceiling and walls (e.g. through the use
of tape, foam or other means which
create tight seals), thus effectively
creating a separate enclosure. This type
of vertical containment acts as the
functional equivalent of a wall for
purposes of defining the work area and,
if the vertical containment meets these
criteria, the floor containment measures
may stop at the edge of the vertical
barrier. However, unlike permanent
walls, vertical containment barriers are
subject to all containment cleaning
requirements including misting, inward
folding, sealing, and proper disposal
following the renovation. A firm must
also thoroughly clean an additional two
feet beyond the vertically-contained
work area. Finally, during ingress or
egress from the vertical enclosure, a firm
must take precaution to ensure that dust
and debris on personnel, tools, and
other items do not escape the work area.
Upon further consideration of the
proposed definition of containment,
particularly in light of the comments
received on the proposed vertical
containment requirements, EPA has
determined that a broader definition of
containment is unnecessary, and may
even be confusing, but a definition of
vertical containment would help to
clarify the vertical containment
requirements. In addition, EPA believes
that there may be confusion among the
regulated community and other
stakeholders about what EPA means
when it uses the term ‘‘vertical
containment.’’ As previously discussed,
vertical containment can span the range
from simple barriers to box-like
structures to more extensive scaffolding.
Accordingly, EPA is promulgating a
definition of ‘‘vertical containment’’ that
is similar to the last sentence of the
proposed definition of ‘‘containment.’’
Vertical containment is defined as a
vertical barrier consisting of plastic
sheeting or other impermeable material
over scaffolding or a rigid frame, or an
equivalent system of containing the
work area. The definition further states
that vertical containment is required for
some exterior renovations but it may be
used on any renovation. EPA
encourages members of the regulated
community, or other stakeholders, who
have questions on the work area
containment requirements or any other
aspect of the RRP rule to consult the
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Frequent Question database accessible
from EPA’s primary lead Web page at
https://www.epa.gov/lead or contact the
National Lead Information Center by
calling 1(800) 424–LEAD [5323].
Hearing- or speech-impaired persons
may reach the National Lead
Information Center through TTY by
calling the toll-free Federal Relay
Service at 1–800–877–8339.
7. Prohibited or restricted practices. In
May 2010, EPA proposed to make a
number of minor revisions to clarify the
prohibitions and restrictions on work
practices in 40 CFR 745.85(a)(3). The
first was a clarification that these
prohibitions and restrictions, e.g., the
prohibition on open flame burning or
torching, apply to all painted surfaces,
not just surfaces where the presence of
lead-based paint has been confirmed.
The term ‘‘lead-based paint’’ was
incorrectly and inadvertently used in
this subparagraph, making it
inconsistent with the rest of the RRP
rule, which applies in the presence of
known lead-based paint as well as paint
that has not been tested for lead content.
Accordingly, EPA proposed to replace
the term ‘‘lead-based paint’’ with
‘‘painted surfaces’’ in this subparagraph.
Of course, if the painted surface has
been tested and found to be free of leadbased paint, the prohibitions and
restrictions on work practices in the
final RRP rule do not apply.
Commenters generally supported this
revision, although two commenters
noted that EPA uses the term ‘‘painted
surfaces’’ throughout the RRP rule and
it is unclear whether this refers just to
paint or to other surface coatings as
well. These commenters noted that the
definition of ‘‘lead-based paint’’
includes paint and other surface
coatings but there is no definition of the
term ‘‘painted surfaces.’’ These
commenters observed that other surface
coatings, such as varnish, can contain
significant amounts of lead. The
commenters suggested that EPA address
this issue throughout the RRP rule. EPA
agrees with these commenters. In using
the term ‘‘painted surfaces,’’ EPA has
always meant component surfaces that
are covered in whole or in part with a
coating that could be lead-based paint.
The term was designed to encompass
situations where the surface is covered
with lead-based paint as defined by the
regulation as well as situations where
the lead content of the surface coating
had not been determined. EPA never
intended to exclude varnishes or other
surface coatings from the coverage of the
RRP rule. In fact, the applicability
section of the RRP rule, 40 CFR 745.82,
limits the exclusions for testing to those
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situations where the components to be
disturbed by a renovation have been
demonstrated to be free of paint and
other surface coatings that contain lead
at levels equal to or exceeding the
regulatory threshold. Therefore, EPA is
promulgating this revision as proposed
and EPA is also adding a clarifying
definition of ‘‘painted surface’’ to 40
CFR 745.83. This definition states that
painted surface means a component
surface covered in whole or in part with
paint or other surface coatings.
In addition, EPA proposed to clarify
that the restriction in this section on the
use of machines that remove paint
through high speed operation applies
anywhere painted surfaces are being
disturbed by such machines; the
restriction is not limited to situations
where all of the paint is removed by
such machines. EPA received no
comments specifically on this proposed
revision, although the comments on the
general issue of paint including other
surface coatings are also applicable
here. EPA is promulgating this revision
as proposed, with the addition of the
phrase ‘‘or other surface coatings’’ after
the term ‘‘paint,’’ because EPA never
intended to create a loophole that would
allow someone to remove some or most
of the paint or other surface coating
from a component without complying
with the restriction.
Finally, EPA proposed to clarify what
was meant by HEPA exhaust control. In
order to better express what is required
when machines designed to remove
paint through high speed operation are
used, EPA consulted the Occupational
Safety and Health Administration’s
Technical Manual (Ref. 12). The use of
shrouded tools to remove lead-based
paint is discussed in Chapter 3 of
Section V, entitled ‘‘Controlling Lead
Exposures in the Construction Industry:
Engineering and Work Practice
Controls.’’ Using language from this
reference, EPA proposed to amend 40
CFR 745.85(a)(3)(ii) to read, ‘‘The use of
machines designed to remove paint
through high speed operation such as
sanding, grinding, power planing,
needle gun, abrasive blasting, or
sandblasting, is prohibited on painted
surfaces unless such machines are used
shrouded and equipped with a HEPA
vacuum attachment to collect dust and
debris at the point of generation.’’ EPA
received several comments on this
topic. The commenters generally
supported the change, but two thought
that there should be a performance
standard included in the provision, a
visible standard that warns the workers
that the shroud or containment system
is not working properly. EPA agrees
with these commenters. Another
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commenter thought that the term
‘‘shrouded’’ in the proposed revision
would make the RRP rule more stringent
than the requirements applicable to
abatement contractors. After consulting
the abatement chapter of the HUD
Guidelines, EPA has determined that
the proposed language could potentially
be read to exclude one of the two types
of sanders described by HUD as
appropriate for abatement work because
they provide HEPA exhaust control.
Accordingly, EPA is promulgating the
revision as proposed, except that the
regulatory language will read ‘‘* * *
unless such machines have shrouds or
containment systems and are equipped
with a HEPA vacuum attachment to
collect dust and debris at the point of
generation. Machines must be operated
so that no visible dust or release of air
occurs outside the shroud or
containment system.’’
8. HEPA vacuums. In May 2010, EPA
proposed to clarify that vacuums
qualifying as HEPA vacuums for the
purposes of this rule must be operated
and maintained in accordance with the
manufacturer’s instructions in order to
continue to qualify as HEPA vacuums.
This includes following the
manufacturer’s filter change interval
recommendations. EPA also proposed to
clarify that the standard for HEPA
filters, that they be capable of capturing
particles of 0.3 microns with 99.97%
efficiency, means that the filters must
have a Minimum Efficiency Reporting
Value (MERV) of 17 or greater. At the
time, EPA also recommended that
renovation firms have information from
the manufacturer that the particular
model of vacuum that the renovation
firm intends to use, or the vacuum’s
HEPA filter, has been tested in
accordance with an applicable test
method, such as ASTM F1471–09,
‘‘Standard Test Method for Air Cleaning
Performance of a High-Efficiency
Particulate Air-Filter System,’’ and has
been determined to meet this standard
(Ref. 13).
EPA received a number of comments
on these proposed revisions.
Commenters specifically addressing the
requirement that vacuums be operated
in accordance with the manufacturer’s
instructions, including filter change
interval recommendations, were in
general agreement with the requirement.
Other commenters expressed a general
concern that these revisions would
prohibit the use of consumer-grade
HEPA vacuums that renovation firms
had recently purchased to comply with
the RRP rule. Some argued that the
proposed language regarding the MERV
was too stringent, given industry
practice for high-efficiency vacuums.
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One commenter cited research they had
done on the efficiency of HEPA
vacuums to argue that the HEPA
vacuums used in EPA’s Dust Study
would not have met the MERV standard
proposed by EPA. However, the
commenter did not provide sufficient
information to support this assertion.
Several commenters echoed comments
EPA received during the rulemaking
process for the 2008 RRP rule, arguing
that HEPA vacuums are too expensive
and are not necessary. Other
commenters believed that additional
requirements should be added, such as
a requirement to field test the efficiency
of the vacuums on a regular basis or
after filter changes.
EPA continues to believe that HEPA
vacuums are a necessary part of the
required RRP work practices. In
addition, the OSHA Lead in
Construction standard requires the use
of HEPA vacuums whenever vacuums
are used. However, EPA also
understands the concerns of those
commenters who had already purchased
HEPA vacuums for purposes of the RRP
rule as well as those others who thought
that the proposed MERV value of 17
would be too stringent. In balancing
these concerns, EPA has decided to
promulgate the requirement that HEPA
vacuums be operated in accordance
with manufacturer’s instructions, but
not the requirement that compliant
vacuums be rated at a MERV value of 17
or higher.
In addition, in response to EPA’s
recommendation that renovation firms
obtain information from the
manufacturer that the efficiency of their
particular model of HEPA vacuum or
HEPA filter has been tested in
accordance with an applicable test
method, some commenters noted that
this information may not be readily
available to renovation firms. These
commenters suggested that EPA
maintain a list of HEPA vacuums that
have been tested and found to meet the
HEPA vacuum requirements.
9. On-the-job training. EPA’s 2010
proposal included a clarification
regarding the required elements of onthe-job training provided by renovators.
Specifically, EPA proposed to clarify
that the RRP rule requires certified
renovators to train other renovation
workers in only the work practices
required by the RRP rule that the
workers will be using in performing
their assigned tasks. As discussed in the
2010 proposal, EPA did not intend to
require training in any other subjects,
such as how to paint or how to connect
pipes. EPA is promulgating the
clarification as proposed and amending
40 CFR 745.90(b)(2) and (b)(4) to refer
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specifically to the work practice
requirements in 40 CFR 745.85(a). Two
comments were received on this
proposed clarification, both commenters
expressed support for the change.
10. Grandfathering. Under the final
2008 RRP rule, individuals who
successfully completed an accredited
abatement worker or supervisor course,
and individuals who successfully
completed the HUD, EPA, or the joint
EPA/HUD model renovation training
courses may take an accredited refresher
renovation training course in lieu of the
initial renovation training to become a
certified renovator. In addition,
individuals who have successfully
completed an accredited lead-based
paint inspector or risk assessor course,
but are not currently certified in the
discipline, may take an accredited
refresher dust sampling technician
course in lieu of the initial training to
become a certified dust sampling
technician. As discussed in the 2010
proposal, EPA inadvertently failed to
include in the 2008 RRP rule a time
limit for taking the refresher in lieu of
the initial course. Many of the
commenters who addressed the issue of
grandfathering in the 2008 RRP
rulemaking contended that there should
be restrictions based on how much time
elapsed since the training was taken. In
addition, under the lead-based paint
activities regulations at 40 CFR 745.226,
EPA allowed a similar grandfathering
provision but only for a limited time.
Accordingly, EPA proposed to set a
limit on when an individual can take
advantage of the grandfathering
provision under the RRP rule. The
preamble to the 2010 proposal stated
that the limit would be July 31, 2011,
such that renovators and dust sampling
technicians who take the appropriate
prerequisite course before that date
would be permitted to take an
accredited refresher training course in
lieu of the initial training. EPA received
three comments on this provision. One
commenter helpfully pointed out that,
while the preamble said that the limit
would be July 31, 2011, the proposed
regulatory text said that it would be
April 22, 2011. The three commenters
supported the limit of July 31, 2011, one
noting that EPA should not continue to
encourage renovators to take lead-safe
work practices courses that do not meet
the requirements for certified renovator
training. EPA generally agrees with
these commenters and is promulgating a
provision that allows renovators and
dust sampling technicians who take the
appropriate prerequisite course before
the effective date of this rule to take an
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accredited refresher training course in
lieu of the initial training.
EPA also proposed a clarification
regarding the grandfathering provision
as it applies to the dust sampling
technician discipline. Individuals who
successfully complete an accredited
lead-based paint inspector or risk
assessor course, but are not currently
certified in the discipline, may take an
accredited refresher dust sampling
technician course in lieu of the initial
training before the effective date of this
rule to become a certified dust sampling
technician. Inspectors and risk assessors
who are certified by EPA or an
authorized state program are qualified to
perform dust sampling as part of lead
hazard screens, risk assessments, or
abatements as well as for other
purposes, such as post-renovation dust
sampling. Therefore, it would be
unnecessary for a certified inspector or
risk assessor to seek certification as a
dust sampling technician. The 2008 RRP
rule explains who is eligible to take the
refresher dust sampling technician
course in lieu of the initial training.
However, the regulations as
promulgated did not explicitly say that
a certified inspector or risk assessor may
perform dust sampling. In order to
clarify the intent of the regulation, EPA
proposed to amend 40 CFR 745.90(a)(3)
to specifically state that a certified
inspector or risk assessor may act as a
dust sampling technician. EPA is
promulgating this provision as
proposed. One comment was received
on this topic expressing general support
for the amendment.
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III. References
As indicated under ADDRESSES, a
docket has been established for this
rulemaking under docket ID number
EPA–HQ–OPPT–2005–0049. The
following is a listing of the documents
that are specifically referenced in this
final rule. The docket includes these
documents and other information
considered by EPA, including
documents that are referenced within
the documents that are included in the
docket, even if the referenced document
is not physically located in the docket.
For assistance in locating these other
documents, please consult the technical
contact listed under FOR FURTHER
INFORMATION CONTACT.
1. U.S. Environmental Protection Agency
(EPA). Lead; Clearance and Clearance
Testing Requirements for the
Renovation, Repair, and Painting
Program; Proposed Rule. Federal
Register (75 FR 25038, May 6, 2010)
(FRL–8823–5).
2. EPA. Lead; Renovation, Repair, and
Painting Program; Final Rule. Federal
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Register (73 FR 21692, April 22, 2008)
(FRL–8355–7).
3. EPA. Lead; Requirements for Lead-based
Paint Activities; Final Rule. Federal
Register (61 FR 45778), August 29, 1996)
(FRL–5389–9).
4. EPA. Lead; Identification of Dangerous
Levels of Lead; Final Rule. Federal
Register (66 FR 1206, January 5, 2001)
(FRL–6763–5).
5. EPA. Electrostatic Cloth and Wet Cloth
Field Study in Residential Housing
(September 2005).
6. EPA. Characterization of Dust Lead Levels
After Renovation, Repair, and Painting
Activities. (November 13, 2007).
7. EPA. Lead Exposure Associated With
Renovation and Remodeling Activities:
Phase I, Environmental Field Sampling
Study (EPA 747–R–96–007, May 1997).
8. EPA. Reviewed Studies Pertaining to
HEPA Shroud Effectiveness. (2009).
9. EPA. Office of Pollution Prevention and
Toxics (OPPT). ‘‘Economic Analysis for
the TSCA Lead Renovation, Repair, and
Painting Program Final Rule for Target
Housing and Child-Occupied Facilities’’
(March 2008).
10. U.S. Department of Housing and Urban
Development (HUD). Evaluation of the
HUD Lead-Based Paint Hazard Control
Grant Program: Final Report. May 1,
2004.
11. HUD. Guidelines for the Evaluation and
Control of Lead-Based Paint Hazards in
Housing (June 1995).
12. U.S. Department of Labor, Occupational
Safety and Health Administration
(OSHA). Technical Manual TED 01–00–
015 [TED 1–0.15A]. Revised June 24,
2008.
13. ASTM International. Standard Test
Method for Air Cleaning Performance of
a High-Efficiency Particulate Air-Filter
System (F1471–09).
14. EPA. OPPT. ‘‘Discussion of Potential
Costs and Benefits Associated with the
Clearance and Clearance Testing
Requirements for the Renovation, Repair,
and Painting Program Final Rule’’ (July
2011).
15. EPA. OPPT. ‘‘Economic Analysis for the
TSCA Lead Renovation, Repair, and
Painting Program Opt-out and
Recordkeeping Final Rule for Target
Housing and Child-Occupied Facilities’’
(April 2010).
16. EPA. Final Clearance Rule ICR
Addendum for the rulemaking entitled
Lead; Clearance and Clearance Testing
Requirements for the Renovation, Repair,
and Painting Program; Final Rule. (July
2011).
17. EPA. Report of the Small Business
Advocacy Review Panel on the Leadbased Paint Certification and Training;
Renovation and Remodeling
Requirements. (March 3, 2000).
18. EPA. Lead; Renovation, Repair, and
Painting Program; Proposed Rule.
Federal Register (71 FR 1588, January
10, 2006) (FRL–7755–5).
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IV. Statutory and Executive Order
Reviews
A. Regulatory Planning and Review
Under Executive Order 12866,
entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993),
this action is a ‘‘significant regulatory
action.’’ Accordingly, EPA submitted
this action to the Office of Management
and Budget (OMB) for review under
Executive Orders 12866 and 13563,
entitled Improving Regulation and
Regulatory Review (76 FR 3821, January
21, 2011), and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
In addition, EPA prepared a
document discussing the potential costs
and benefits associated with this final
rule. This document, entitled
‘‘Discussion of Potential Costs and
Benefits Associated with the Clearance
and Clearance Testing Requirements for
the Renovation, Repair, and Painting
Program Final Rule’’ (Ref. 14), is
available in the docket for this action
and is briefly summarized here.
For the most part, the amendments to
the RRP rule contained in this final rule
impose only minimal incremental costs.
For example, the requirement for
training course providers to submit
copies of personnel qualifications along
with their applications will result in
providers making copies of and
submitting with their application 2–4
additional pieces of paper that they are
already required to have in their
possession before submitting the
application. The requirement to submit
copies of State training course materials,
if used, could add significantly to the
size of the training provider’s
application. However, EPA believes that
it will be a rare occurrence for training
providers to use State-approved training
course materials, when EPA model
training course materials are readily
available. Likewise, the provision
allowing certified renovators to collect
paint chip samples in lieu of using test
kits adds no additional costs, because
certified renovators are not required to
take this step in addition to existing
activities—it is an added option from
which they may choose. Similarly, the
minimum enforcement provisions and
other requirements for State and Tribal
programs imposes no costs because
States and Tribes are not required to
have authorized programs, nor are they
required to revise their programs to
incorporate EPA revisions. While EPA is
requiring specific recordkeeping for
training providers who wish to provide
e-learning courses, e-learning courses
are not required from any training
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Federal Register / Vol. 76, No. 151 / Friday, August 5, 2011 / Rules and Regulations
provider. In addition, EPA believes that
the recordkeeping requirements for elearning courses are comparable to, and
no more burdensome than, the ordinary
recordkeeping already required for
courses provided in traditional formats.
Many of the amendments are merely
clarifications of existing regulatory
language and implementation of policy
and impose no additional costs.
Examples of these amendments include
the clarifications on the role of the
principal instructor in an accredited
training program, the requirement that
the trainee photograph on a course
completion certificate be an accurate
representation of the trainee and no
smaller than one square inch, and the
clarification that certified renovators are
only required to provide on-the-job
training in the RRP work practices to
other renovation workers.
With respect to the vertical
containment requirements of this final
rule, EPA has already accounted for the
costs of those requirements. In EPA’s
economic analysis for the 2008 RRP
rule, EPA addressed those situations
where the renovation firm must take
extra precautions to effectively contain
dust and debris, including work areas in
close proximity to other buildings, work
areas that abut a property line, and
windy conditions. The 2008 economic
analysis specifically notes that it is
sometimes necessary to erect a system of
vertical containment to prevent paint
dust and debris from contaminating the
ground or any object beyond the work
area. To account for these situations,
EPA estimated that approximately 2%
of exterior jobs would use exterior
containment, and the incremental cost
of vertical containment varies from $330
per wall to $1,640 per wall, depending
on the size of the job. Thus, EPA has
already accounted for the additional
costs incurred for using vertical
containment systems on renovations
performed within 10 feet of the property
line.
This final rule extends the
recordkeeping requirement for providers
of certified renovator and certified dust
sampling technician training from 3
years and 6 months to 5 years in general
and slightly more than 5 years for
training providers who offered
accredited courses in these disciplines
before April 22, 2010. The
recordkeeping extension does not affect
recordkeeping requirements associated
with obtaining and maintaining
accreditation. This extension only
affects those records pertaining to
training courses, specifically
notifications. Pro-rating the
recordkeeping cost estimates from EPA’s
economic analysis for the Opt-Out and
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Recordkeeping Final Rule, also
published in the Federal Register on
May 6, 2010 (Ref. 15), shows that the
recordkeeping burden for courses
provided during the first year the rule
was effective increases from $43.68 to
$61.88 per training provider. For
courses provided in subsequent years,
the recordkeeping burden per training
provider increases from $4.80 to $6.80.
These estimates are for the entire 5 years
that the records would have to be kept.
For the 2008 RRP rule, EPA estimated
that there would be approximately 1.4
million children under the age of 6 and
5.4 million adults who would be
affected by having their exposure to lead
dust minimized due to the rule. The
analysis for the 2010 final Opt-Out rule
estimated that an additional 5.2 million
older children and adults would be
affected by reduced lead exposure due
to the rule.
B. Paperwork Burdens
The information collection
requirements contained in this rule have
been submitted for approval to the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act (PRA), 44 U.S.C. 3501 et seq. EPA
has prepared an Information Collection
Request (ICR) document to amend an
existing ICR that is approved under
OMB Control No. 2070–0155 (EPA ICR
No. 1715). The ICR amendment, entitled
‘‘ICR Addendum for Final Rule entitled
‘‘Lead; Clearance and Clearance Testing
Requirements for the Renovation,
Repair, and Painting Program; Final
Rule (RIN 2070–AJ57)’’ and identified
under EPA ICR No. 2381.02, has been
placed in the docket for this rule (Ref.
16).
This regulatory action contains only
two amendments to the approved
existing information collection:
Amendments to the requirement for the
training provider to submit
documentation of training manager and
principal instructor qualifications; and a
requirement for providers of renovator
and dust sampling technician training to
maintain training records for these
courses for 5 years, rather than 3 years
and 6 months. These requirements add
only negligible paperwork burden hours
to the existing burden estimate.
EPA previously estimated for the final
2008 RRP rule (Ref. 9) and the final Optout rule (Ref. 15) that 170 training
providers would be accredited to
provide renovator training. These
training providers will now have to
submit an additional 2–4 photocopies
along with their applications for
accreditation. EPA estimates that each
photocopy costs $0.09 to generate, for a
maximum of $0.36 additional cost for
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training providers with one training
manager and one principal instructor.
Each of these 170 training providers is
also required to provide training course
notifications under the existing RRP
rule. These notifications will now have
to be kept for 5 years instead of 3 years
and 6 months. EPA has also estimated
that each of these training providers
would offer on average a total of 86
renovator or dust sampling technician
courses in the first year, and 20 per year
thereafter. This would require a total of
182 single-page notifications in the first
year, and 42 each year thereafter.
Under PRA, burden is defined at 5
CFR 1320.3(b) and means the total time,
effort, or financial resources expended
by persons to generate, maintain, retain,
disclose or provide information to or for
a Federal agency. An agency may not
conduct or sponsor, and a person is not
required to respond to a collection of
information unless it displays a
currently valid OMB control number.
The OMB control numbers for EPA’s
regulations codified in 40 CFR chapter
I, after appearing in the preamble of the
final rule, are listed in 40 CFR part 9,
are displayed either by publication in
the Federal Register or by other
appropriate means, such as on the
related collection instrument or form, as
applicable.
C. Small Entity Impacts
Pursuant to section 605(b) of the
Regulatory Flexibility Act (RFA), 5
U.S.C. 601 et seq., the Agency hereby
certifies that this final rule will not have
a significant adverse economic impact
on a substantial number of small
entities. Small entities include small
businesses, small organizations, and
small governmental jurisdictions. For
purposes of assessing the impacts of this
final rule on small entities, small entity
is defined in accordance with RFA
section 601 as:
1. A small business as defined by the
Small Business Administration’s (SBA)
regulations at 13 CFR 121.201.
2. A small governmental jurisdiction
that is a government of a city, county,
town, school district, or special district
with a population of less than 50,000.
3. A small organization that is any
not-for-profit enterprise which is
independently owned and operated and
is not dominant in its field.
The small entities directly regulated
by this final rule are providers of leadbased paint related training, renovation
firms, individuals who perform
renovations, and any small
governmental jurisdictions or not-forprofit enterprises that provide leadbased paint training or renovation
services. As discussed previously, EPA
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has decided not to promulgate the
clearance and clearance testing
requirements, and is instead
promulgating minor amendments to the
requirements for lead-based paint
training providers and renovation firms
that will have only negligible adverse
impacts on any small entities.
In addition, RFA states that agencies
‘‘may consider a series of closely related
rules as one rule for the purposes of [an
IRFA]’’ in order to avoid ‘‘duplicative
action.’’ 5 U.S.C. 605(c). This
rulemaking is closely related to the 2008
RRP rule. Indeed, the proposed rule
addressed one of the major issues in the
2008 rulemaking and some of the
provisions finalized in the 2008 RRP
rule. Accordingly, EPA was not required
to complete a regulatory flexibility
analysis for this rulemaking.
Nonetheless, EPA exercised its
discretion to complete an Initial
Regulatory Flexibility Analysis (IRFA)
for the 2010 proposal (see 75 FR 25038).
The IRFA considered the potential
adverse economic impacts of the 2010
proposed rule on affected small entities,
primarily those related to the proposed
clearance and clearance testing
requirements. The proposed provisions
analyzed for purposes of the IRFA are
not part of this final rule.
Moreover, as discussed in the 2010
proposed rule in more detail, the Small
Business Advocacy Review (SBAR)
Panel that was conducted in connection
with the 2006 RRP proposal is equally
applicable to this closely related
amendment to the 2008 RRP rule. The
SBAR Panel discussed all major aspects
of the 2006 proposal to regulate
renovation and remodeling activities,
including issues related to ensuring that
proper cleanup occurs after renovation
activities. As a part of the panel process,
EPA ‘‘collect[ed] advice and
recommendations’’ from several Small
Entity Representatives (SERs) on the
2006 proposal to regulate renovation
and remodeling activities. 5 U.S.C.
609(b). The SBAR Panel report, entitled
Report of the Small Business Advocacy
Review Panel on The Lead-base
Painting; Certification and Training;
Renovation and Remodeling
Requirements (March 3, 2000),
expressly addressed containment and
dust clearance testing requirements (Ref.
18). Thus, the primary issues considered
in this rulemaking are wholly within the
scope of the issues EPA considered as
part of the 2008 RRP rule and were
within the scope of the issues
considered by the SBAR Panel.
Reconvening the RRP Panel for the 2010
proposed rule would be procedurally
duplicative and unnecessary.
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D. Unfunded Mandates
This rule does not contain a Federal
mandate that may result in expenditures
of $100 million or more for State, local,
and tribal governments, in the aggregate,
or the private sector in any one year.
This rule includes only minor
amendments to the requirements for
providers of lead-based paint training
and for renovation firms. Thus, this rule
is not subject to the requirements of
sections 202 or 205 of the Unfunded
Mandates Reform Act of 1995 (UMRA)
(2 U.S.C. 1531–1538).
This rule is also not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments.
Small governments are only regulated
by this action to the extent that they
engage in providing lead-based paint
training or renovation services.
E. Federalism
Pursuant to Executive Order 13132,
entitled Federalism (64 FR 43255,
August 10, 1999), EPA has determined
that this final rule does not have
‘‘federalism implications,’’ because it
will not have substantial direct effects
on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government, as
specified in Executive Order 13132.
Thus, Executive Order 13132 does not
apply to this final rule. Nevertheless, in
the spirit of the objectives of this
Executive Order, and consistent with
EPA policy to promote communications
between the Agency and State and local
governments, EPA consulted with
representatives of State and local
governments during the rulemaking
process for the 2008 RRP rule. These
consultations are as described in the
preamble to the 2006 RRP proposed rule
(Ref. 18).
F. Indian Tribal Government
Implications
As required by Executive Order
13175, entitled Consultation and
Coordination with Indian Tribal
Governments (59 FR 22951, November
9, 2000), EPA has determined that this
final rule does not have tribal
implications because it will not have
substantial direct effects on Tribal
governments, on the relationship
between the Federal Government and
the Indian Tribes, or on the distribution
of power and responsibilities between
the Federal Government and Indian
Tribes, as specified in the Executive
Order. Thus, Executive Order 13175
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does not apply to this final rule.
Although Executive Order 13175 does
not apply to this final rule, EPA
consulted with Tribal officials and
others by discussing potential
renovation regulatory options at several
national lead program meetings hosted
by EPA and other interested Federal
agencies.
G. Protection of Children
Executive Order 13045, entitled
Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997) does
not apply to this final rule because it is
not an ‘‘economically significant
regulatory action’’ as defined by
Executive Order 12866. While the
environmental health or safety risk
addressed by the 2008 RRP rule does
have a disproportionate effect on
children, this final rule makes only
minor changes in the administrative
requirements for accredited training
providers and includes minor
amendments to the requirements for
renovation firms.
EPA has evaluated the environmental
health or safety effects of renovation,
repair, and painting projects on
children. Various aspects of this
evaluation are discussed in the
preamble to the 2006 proposed RRP rule
(Ref. 18). The primary purpose of the
final 2008 RRP rule is to minimize
exposure to lead-based paint hazards
created during renovation, repair, and
painting activities in housing where
children under age 6 reside and in
housing or other buildings frequented
by children under age 6. In the absence
of the final 2008 RRP rule, adequate
work practices are not likely to be
employed during renovation, repair, and
painting activities. EPA’s analysis
indicates that there will be
approximately 1.4 million children
under age 6 affected by the RRP rule.
These children are projected to receive
considerable benefits due to the RRP
rule. In addition, older children will
also benefit from the protections
afforded by the RRP rule.
H. Effect on Energy Supply, Distribution,
or Use
This final rule is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211, entitled Actions
Concerning Regulations that
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001) because it is not likely to have
any adverse effect on the supply,
distribution, or use of energy.
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I. Technical Standards
This regulatory action does not
involve any technical standards that
would require Agency consideration of
voluntary consensus standards pursuant
to section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), 15 U.S.C. 272
note. Section 12(d) of NTTAA directs
EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, business
practices) that are developed or adopted
by voluntary consensus standards
bodies. NTTAA requires EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
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J. Environmental Justice
Executive Order 12898, entitled
Federal Actions to Address
Environmental Justice in Minority
Populations and Low-Income
Populations (59 FR 7629, February 16,
1994) establishes Federal executive
policy on environmental justice. Its
main provision directs Federal agencies,
to the greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
While EPA has not assessed the
potential impact of this final rule on
minority and low-income populations,
EPA did assess the potential impact of
the final 2008 RRP rule as a whole. As
a result of the final 2008 RRP rule
assessment, contained in the economic
analysis for the final 2008 RRP rule,
EPA has determined that the RRP rule
will not have disproportionately high
and adverse human health or
environmental effects on minority or
low-income populations because it
increases the level of environmental
protection for all affected populations
without having any disproportionately
high and adverse human health or
environmental effects on any
population, including any minority or
low-income population (Ref. 9).
V. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
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that before a rule may take effect, the
agency promulgating the rule must
submit a rule report to each House of
the Congress and the Comptroller
General of the United States. EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of the rule in the Federal
Register. This rule is not a ‘‘major rule’’
as defined by 5 U.S.C. 804(2).
List of Subjects in 40 CFR Part 745
Environmental protection, Childoccupied facility, Housing renovation,
Lead, Lead-based paint, Renovation,
Reporting and recordkeeping
requirements.
Dated: July 15, 2011.
Lisa P. Jackson,
Administrator.
Therefore, 40 CFR chapter I is
amended as follows:
PART 745—[AMENDED]
1. The authority citation for part 745
continues to read as follows:
■
Authority: 15 U.S.C. 2605, 2607, 2681–
2692 and 42 U.S.C. 4852d.
2. In § 745.82, add a new paragraph
(a)(3) to read as follows.
■
§ 745.82
Applicability.
(a) * * *
(3) Renovations in target housing or
child-occupied facilities in which a
certified renovator has collected a paint
chip sample from each painted
component affected by the renovation
and a laboratory recognized by EPA
pursuant to section 405(b) of TSCA as
being capable of performing analyses for
lead compounds in paint chip samples
has determined that the samples are free
of paint or other surface coatings that
contain lead equal to or in excess of 1.0
mg/cm2 or 0.5% by weight. If the
components make up an integrated
whole, such as the individual stair
treads and risers of a single staircase,
the renovator is required to test only one
of the individual components, unless
the individual components appear to
have been repainted or refinished
separately.
*
*
*
*
*
■ 3. In § 745.83, revise the definition of
‘‘HEPA vacuum’’ and add the definition
‘‘Painted surface’’ and the definition
‘‘Vertical containment’’ in alphabetical
order to read as follows:
§ 745.83
*
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Definitions.
*
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*
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*
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HEPA vacuum means a vacuum
cleaner which has been designed with a
high-efficiency particulate air (HEPA)
filter as the last filtration stage. A HEPA
filter is a filter that is capable of
capturing particulates of 0.3 microns
with 99.97% efficiency. The vacuum
cleaner must be designed so that all the
air drawn into the machine is expelled
through the HEPA filter with none of
the air leaking past it. HEPA vacuums
must be operated and maintained in
accordance with the manufacturer’s
instructions.
*
*
*
*
*
Painted surface means a component
surface covered in whole or in part with
paint or other surface coatings.
*
*
*
*
*
Vertical containment means a vertical
barrier consisting of plastic sheeting or
other impermeable material over
scaffolding or a rigid frame, or an
equivalent system of containing the
work area. Vertical containment is
required for some exterior renovations
but it may be used on any renovation.
*
*
*
*
*
■ 4. Section 745.85 is amended as
follows:
■ a. Revise paragraphs (a)(2)(i)(D) and
(a)(2)(ii)(C) and (D);
■ b. Revise paragraph (a)(3);
The revisions read as follows:
§ 745.85
Work practice standards.
(a) * * *
(2) * * *
(i) * * *
(D) Cover the floor surface, including
installed carpet, with taped-down
plastic sheeting or other impermeable
material in the work area 6 feet beyond
the perimeter of surfaces undergoing
renovation or a sufficient distance to
contain the dust, whichever is greater.
Floor containment measures may stop at
the edge of the vertical barrier when
using a vertical containment system
consisting of impermeable barriers that
extend from the floor to the ceiling and
are tightly sealed at joints with the floor,
ceiling and walls.
*
*
*
*
*
(ii) * * *
(C) Cover the ground with plastic
sheeting or other disposable
impermeable material extending 10 feet
beyond the perimeter of surfaces
undergoing renovation or a sufficient
distance to collect falling paint debris,
whichever is greater, unless the
property line prevents 10 feet of such
ground covering. Ground containment
measures may stop at the edge of the
vertical barrier when using a vertical
containment system.
(D) If the renovation will affect
surfaces within 10 feet of the property
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line, the renovation firm must erect
vertical containment or equivalent extra
precautions in containing the work area
to ensure that dust and debris from the
renovation does not contaminate
adjacent buildings or migrate to adjacent
properties. Vertical containment or
equivalent extra precautions in
containing the work area may also be
necessary in other situations in order to
prevent contamination of other
buildings, other areas of the property, or
adjacent buildings or properties.
(3) Prohibited and restricted practices.
The work practices listed below are
prohibited or restricted during a
renovation as follows:
(i) Open-flame burning or torching of
painted surfaces is prohibited.
(ii) The use of machines designed to
remove paint or other surface coatings
through high speed operation such as
sanding, grinding, power planing,
needle gun, abrasive blasting, or
sandblasting, is prohibited on painted
surfaces unless such machines have
shrouds or containment systems and are
equipped with a HEPA vacuum
attachment to collect dust and debris at
the point of generation. Machines must
be operated so that no visible dust or
release of air occurs outside the shroud
or containment system.
(iii) Operating a heat gun on painted
surfaces is permitted only at
temperatures below 1,100 degrees
Fahrenheit.
*
*
*
*
*
■ 5. Section 745.86 is amended as
follows:
a. Add paragraph (b)(1)(iii).
b. Redesignate paragraphs (b)(6)(iv)
through (vii) as paragraphs (b)(6)(v)
through (viii), respectively.
c. Add new paragraph (b)(6)(iv).
The additions and revisions read as
follows:
§ 745.86 Recordkeeping and reporting
requirements.
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*
*
*
*
*
(b) * * *
(1) * * *
(iii) Records prepared by a certified
renovator after collecting paint chip
samples, including a description of the
components that were tested including
their locations, the name and address of
the NLLAP-recognized entity
performing the analysis, and the results
for each sample.
*
*
*
*
*
(6) * * *
(iv) If paint chip samples were
collected, that the samples were
collected at the specified locations, that
the specified NLLAP-recognized
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laboratory analyzed the samples, and
that the results were as specified.
*
*
*
*
*
■ 6. Section 745.90 is amended as
follows:
■ a. Revise paragraphs (a)(2) and (a)(3).
■ b. Revise paragraphs (b)(2), (b)(4), and
(b)(8).
§ 745.90 Renovator certification and dust
sampling technician certification.
(a) * * *
(2) Individuals who have successfully
completed an accredited abatement
worker or supervisor course, or
individuals who successfully completed
an EPA, HUD, or EPA/HUD model
renovation training course before
October 4, 2011 may take an accredited
refresher renovator training course in
lieu of the initial renovator training
course to become a certified renovator.
(3) Individuals who have successfully
completed an accredited lead-based
paint inspector or risk assessor course
October 4, 2011 may take an accredited
refresher dust sampling technician
course in lieu of the initial training to
become a certified dust sampling
technician. Individuals who are
currently certified as lead-based paint
inspectors or risk assessors may act as
certified dust sampling technicians
without further training.
*
*
*
*
*
(b) * * *
(2) Must provide training to workers
on the work practices required by
§ 745.85(a) that they will be using in
performing their assigned tasks.
*
*
*
*
*
(4) Must regularly direct work being
performed by other individuals to
ensure that the work practices required
by § 745.85(a) are being followed,
including maintaining the integrity of
the containment barriers and ensuring
that dust or debris does not spread
beyond the work area.
*
*
*
*
*
(8) Must prepare the records required
by § 745.86(b)(1)(ii) and (6).
*
*
*
*
*
■ 7. In § 745.92, add paragraph (b)(3) to
read as follows:
§ 745.92 Fees for the accreditation of
renovation and dust sampling technician
training and the certification of renovation
firms.
*
*
*
*
*
(b) * * *
(3) Accreditation or certification
amendments. No fee will be charged for
accreditation or certification
amendments.
*
*
*
*
*
■ 8. Revise § 745.225 to read as follows:
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§ 745.225 Accreditation of training
programs: target housing and child
occupied facilities.
(a) Scope. (1) A training program may
seek accreditation to offer courses in
any of the following disciplines:
Inspector, risk assessor, supervisor,
project designer, abatement worker,
renovator, and dust sampling
technician. A training program may also
seek accreditation to offer refresher
courses for each of the above listed
disciplines.
(2) Training programs may first apply
to EPA for accreditation of their leadbased paint activities courses or
refresher courses pursuant to this
section on or after August 31, 1998.
Training programs may first apply to
EPA for accreditation of their renovator
or dust sampling technician courses or
refresher courses pursuant to this
section on or after April 22, 2009.
(3) A training program must not
provide, offer, or claim to provide EPAaccredited lead-based paint activities
courses without applying for and
receiving accreditation from EPA as
required under paragraph (b) of this
section on or after March 1, 1999. A
training program must not provide,
offer, or claim to provide EPAaccredited renovator or dust sampling
technician courses without applying for
and receiving accreditation from EPA as
required under paragraph (b) of this
section on or after June 23, 2008.
(b) Application process. The
following are procedures a training
program must follow to receive EPA
accreditation to offer lead-based paint
activities courses, renovator courses, or
dust sampling technician courses:
(1) A training program seeking
accreditation shall submit a written
application to EPA containing the
following information:
(i) The training program’s name,
address, and telephone number.
(ii) A list of courses for which it is
applying for accreditation. For the
purposes of this section, courses taught
in different languages and electronic
learning courses are considered
different courses, and each must
independently meet the accreditation
requirements.
(iii) The name and documentation of
the qualifications of the training
program manager.
(iv) The name(s) and documentation
of qualifications of any principal
instructor(s).
(v) A statement signed by the training
program manager certifying that the
training program meets the
requirements established in paragraph
(c) of this section. If a training program
uses EPA-recommended model training
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materials, or training materials
approved by a State or Indian Tribe that
has been authorized by EPA under
subpart Q of this part, the training
program manager shall include a
statement certifying that, as well.
(vi) If a training program does not use
EPA-recommended model training
materials, its application for
accreditation shall also include:
(A) A copy of the student and
instructor manuals, or other materials to
be used for each course.
(B) A copy of the course agenda for
each course.
(C) When applying for accreditation of
a course in a language other than
English, a signed statement from a
qualified, independent translator that
they had compared the course to the
English language version and found the
translation to be accurate.
(vii) All training programs shall
include in their application for
accreditation the following:
(A) A description of the facilities and
equipment to be used for lecture and
hands-on training.
(B) A copy of the course test blueprint
for each course.
(C) A description of the activities and
procedures that will be used for
conducting the assessment of hands-on
skills for each course.
(D) A copy of the quality control plan
as described in paragraph (c)(9) of this
section.
(2) If a training program meets the
requirements in paragraph (c) of this
section, then EPA shall approve the
application for accreditation no more
than 180 days after receiving a complete
application from the training program.
In the case of approval, a certificate of
accreditation shall be sent to the
applicant. In the case of disapproval, a
letter describing the reasons for
disapproval shall be sent to the
applicant. Prior to disapproval, EPA
may, at its discretion, work with the
applicant to address inadequacies in the
application for accreditation. EPA may
also request additional materials
retained by the training program under
paragraph (i) of this section. If a training
program’s application is disapproved,
the program may reapply for
accreditation at any time.
(3) A training program may apply for
accreditation to offer courses or
refresher courses in as many disciplines
as it chooses. A training program may
seek accreditation for additional courses
at any time as long as the program can
demonstrate that it meets the
requirements of this section.
(4) A training program applying for
accreditation must submit the
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appropriate fees in accordance with
§ 745.238.
(c) Requirements for the accreditation
of training programs. For a training
program to obtain accreditation from
EPA to offer lead-based paint activities
courses, renovator courses, or dust
sampling technician courses, the
program must meet the following
requirements:
(1) The training program shall employ
a training manager who has:
(i) At least 2 years of experience,
education, or training in teaching
workers or adults; or
(ii) A bachelor’s or graduate degree in
building construction technology,
engineering, industrial hygiene, safety,
public health, education, business
administration or program management
or a related field; or
(iii) Two years of experience in
managing a training program
specializing in environmental hazards;
and
(iv) Demonstrated experience,
education, or training in the
construction industry including: Lead or
asbestos abatement, painting, carpentry,
renovation, remodeling, occupational
safety and health, or industrial hygiene.
(2) The training manager shall
designate a qualified principal
instructor for each course who has:
(i) Demonstrated experience,
education, or training in teaching
workers or adults; and
(ii) Successfully completed at least 16
hours of any EPA-accredited or EPAauthorized State or Tribal-accredited
lead-specific training for instructors of
lead-based paint activities courses or 8
hours of any EPA-accredited or EPAauthorized State or Tribal-accredited
lead-specific training for instructors of
renovator or dust sampling technician
courses; and
(iii) Demonstrated experience,
education, or training in lead or asbestos
abatement, painting, carpentry,
renovation, remodeling, occupational
safety and health, or industrial hygiene.
(3) The principal instructor shall be
responsible for the organization of the
course, course delivery, and oversight of
the teaching of all course material. The
training manager may designate guest
instructors as needed for a portion of the
course to provide instruction specific to
the lecture, hands-on activities, or work
practice components of a course.
However, the principal instructor is
primarily responsible for teaching the
course materials and must be present to
provide instruction (or oversight of
portions of the course taught by guest
instructors) for the course for which he
has been designated the principal
instructor.
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(4) The following documents shall be
recognized by EPA as evidence that
training managers and principal
instructors have the education, work
experience, training requirements or
demonstrated experience, specifically
listed in paragraphs (c)(1) and (c)(2) of
this section. This documentation must
be submitted with the accreditation
application and retained by the training
program as required by the
recordkeeping requirements contained
in paragraph (i) of this section. Those
documents include the following:
(i) Official academic transcripts or
diploma as evidence of meeting the
education requirements.
(ii) Resumes, letters of reference, or
documentation of work experience, as
evidence of meeting the work
experience requirements.
(iii) Certificates from train-the-trainer
courses and lead-specific training
courses, as evidence of meeting the
training requirements.
(5) The training program shall ensure
the availability of, and provide adequate
facilities for, the delivery of the lecture,
course test, hands-on training, and
assessment activities. This includes
providing training equipment that
reflects current work practices and
maintaining or updating the equipment
and facilities as needed.
(6) To become accredited in the
following disciplines, the training
program shall provide training courses
that meet the following training
requirements:
(i) The inspector course shall last a
minimum of 24 training hours, with a
minimum of 8 hours devoted to handson training activities. The minimum
curriculum requirements for the
inspector course are contained in
paragraph (d)(1) of this section.
(ii) The risk assessor course shall last
a minimum of 16 training hours, with a
minimum of 4 hours devoted to handson training activities. The minimum
curriculum requirements for the risk
assessor course are contained in
paragraph (d)(2) of this section.
(iii) The supervisor course shall last a
minimum of 32 training hours, with a
minimum of 8 hours devoted to handson activities. The minimum curriculum
requirements for the supervisor course
are contained in paragraph (d)(3) of this
section.
(iv) The project designer course shall
last a minimum of 8 training hours. The
minimum curriculum requirements for
the project designer course are
contained in paragraph (d)(4) of this
section.
(v) The abatement worker course shall
last a minimum of 16 training hours,
with a minimum of 8 hours devoted to
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hands-on training activities. The
minimum curriculum requirements for
the abatement worker course are
contained in paragraph (d)(5) of this
section.
(vi) The renovator course must last a
minimum of 8 training hours, with a
minimum of 2 hours devoted to handson training activities. The minimum
curriculum requirements for the
renovator course are contained in
paragraph (d)(6) of this section.
(vii) The dust sampling technician
course must last a minimum of 8
training hours, with a minimum of 2
hours devoted to hands-on training
activities. The minimum curriculum
requirements for the dust sampling
technician course are contained in
paragraph (d)(7) of this section.
(viii) Electronic learning and other
alternative course delivery methods are
permitted for the classroom portion of
renovator, dust sampling technician, or
lead-based paint activities courses but
not the hands-on portion of these
courses, or for final course tests or
proficiency tests described in paragraph
(c)(7) of this section. Electronic learning
courses must comply with the following
requirements:
(A) A unique identifier must be
assigned to each student for them to use
to launch and re-launch the course.
(B) The training provider must track
each student’s course log-ins, launches,
progress, and completion, and maintain
these records in accordance with
paragraph (i) of this section.
(C) The course must include periodic
knowledge checks equivalent to the
number and content of the knowledge
checks contained in EPA’s model
course, but at least 16 over the entire
course. The knowledge checks must be
successfully completed before the
student can go on to the next module.
(D) There must be a test of at least 20
questions at the end of the electronic
learning portion of the course, of which
80% must be answered correctly by the
student for successful completion of the
electronic learning portion of the
course. The test must be designed so
that students to do not receive feedback
on their test answers until after they
have completed and submitted the test.
(E) Each student must be able to save
or print a copy of an electronic learning
course completion certificate. The
electronic certificate must not be
susceptible to easy editing.
(7) For each course offered, the
training program shall conduct either a
course test at the completion of the
course, and if applicable, a hands-on
skills assessment, or in the alternative,
a proficiency test for that discipline.
Each student must successfully
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complete the hands-on skills assessment
and receive a passing score on the
course test to pass any course, or
successfully complete a proficiency test.
(i) The training manager is
responsible for maintaining the validity
and integrity of the hands-on skills
assessment or proficiency test to ensure
that it accurately evaluates the trainees’
performance of the work practices and
procedures associated with the course
topics contained in paragraph (d) of this
section.
(ii) The training manager is
responsible for maintaining the validity
and integrity of the course test to ensure
that it accurately evaluates the trainees’
knowledge and retention of the course
topics.
(iii) The course test shall be
developed in accordance with the test
blueprint submitted with the training
accreditation application.
(8) The training program shall issue
unique course completion certificates to
each individual who passes the training
course. The course completion
certificate shall include:
(i) The name, a unique identification
number, and address of the individual.
(ii) The name of the particular course
that the individual completed.
(iii) Dates of course completion/test
passage.
(iv) For initial inspector, risk assessor,
project designer, supervisor, or
abatement worker course completion
certificates, the expiration date of
interim certification, which is 6 months
from the date of course completion.
(v) The name, address, and telephone
number of the training program.
(vi) The language in which the course
was taught.
(vii) For renovator and dust sampling
technician course completion
certificates, a photograph of the
individual. The photograph must be an
accurate and recognizable image of the
individual. As reproduced on the
certificate, the photograph must not be
smaller than 1 square inch.
(9) The training manager shall
develop and implement a quality
control plan. The plan shall be used to
maintain and improve the quality of the
training program over time. This plan
shall contain at least the following
elements:
(i) Procedures for periodic revision of
training materials and the course test to
reflect innovations in the field.
(ii) Procedures for the training
manager’s annual review of principal
instructor competency.
(10) Courses offered by the training
program must teach the work practice
standards contained in § 745.85 or
§ 745.227, as applicable, in such a
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manner that trainees are provided with
the knowledge needed to perform the
renovations or lead-based paint
activities they will be responsible for
conducting.
(11) The training manager shall be
responsible for ensuring that the
training program complies at all times
with all of the requirements in this
section.
(12) The training manager shall allow
EPA to audit the training program to
verify the contents of the application for
accreditation as described in paragraph
(b) of this section.
(13) The training manager must
provide notification of renovator, dust
sampling technician, or lead-based paint
activities courses offered.
(i) The training manager must provide
EPA with notification of all renovator,
dust sampling technician, or lead-based
paint activities courses offered. The
original notification must be received by
EPA at least 7 business days prior to the
start date of any renovator, dust
sampling technician, or lead-based paint
activities course.
(ii) The training manager must
provide EPA updated notification when
renovator, dust sampling technician, or
lead-based paint activities courses will
begin on a date other than the start date
specified in the original notification, as
follows:
(A) For renovator, dust sampling
technician, or lead-based paint activities
courses beginning prior to the start date
provided to EPA, an updated
notification must be received by EPA at
least 7 business days before the new
start date.
(B) For renovator, dust sampling
technician, or lead-based paint activities
courses beginning after the start date
provided to EPA, an updated
notification must be received by EPA at
least 2 business days before the start
date provided to EPA.
(iii) The training manager must
update EPA of any change in location of
renovator, dust sampling technician, or
lead-based paint activities courses at
least 7 business days prior to the start
date provided to EPA.
(iv) The training manager must update
EPA regarding any course cancellations,
or any other change to the original
notification. Updated notifications must
be received by EPA at least 2 business
days prior to the start date provided to
EPA.
(v) Each notification, including
updates, must include the following:
(A) Notification type (original, update,
cancellation).
(B) Training program name, EPA
accreditation number, address, and
telephone number.
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(C) Course discipline, type (initial/
refresher), and the language in which
instruction will be given.
(D) Date(s) and time(s) of training.
(E) Training location(s) telephone
number, and address.
(F) Principal instructor’s name.
(G) Training manager’s name and
signature.
(vi) Notification must be
accomplished using any of the following
methods: Written notification, or
electronically using the Agency’s
Central Data Exchange (CDX). Written
notification of lead-based paint
activities course schedules can be
accomplished by using either the
sample form titled ‘‘Lead-Based Paint
Training Notification’’ or a similar form
containing the information required in
paragraph (c)(13)(v) of this section. All
written notifications must be delivered
to EPA by U.S. Postal Service, fax,
commercial delivery service, or hand
delivery (persons submitting
notification by U.S. Postal Service are
reminded that they should allow 3
additional business days for delivery in
order to ensure that EPA receives the
notification by the required date).
Instructions and sample forms can be
obtained from the NLIC at 1–800–424–
LEAD(5323), or on the Internet at
https://www.epa.gov/lead. Hearing- or
speech-impaired persons may reach the
above telephone number through TTY
by calling the toll-free Federal Relay
Service at 1–800–877–8339.
(vii) Renovator, dust sampling
technician, or lead-based paint activities
courses must not begin on a date, or at
a location other than that specified in
the original notification unless an
updated notification identifying a new
start date or location is submitted, in
which case the course must begin on the
new start date and/or location specified
in the updated notification.
(viii) No training program shall
provide renovator, dust sampling
technician, or lead-based paint activities
courses without first notifying EPA of
such activities in accordance with the
requirements of this paragraph.
(14) The training manager must
provide notification following
completion of renovator, dust sampling
technician, or lead-based paint activities
courses.
(i) The training manager must provide
EPA notification after the completion of
any lead-based paint activities course.
This notice must be received by EPA no
later than 10 business days following
course completion.
(ii) The notification must include the
following:
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(A) Training program name, EPA
accreditation number, address, and
telephone number.
(B) Course discipline and type
(initial/refresher).
(C) Date(s) of training.
(D) The following information for
each student who took the course:
(1) Name.
(2) Address.
(3) Date of birth.
(4) Course completion certificate
number.
(5) Course test score.
(6) For renovator or dust sampling
technician courses, a digital photograph
of the student.
(E) Training manager’s name and
signature.
(iii) Notification must be
accomplished using any of the following
methods: Written notification, or
electronically using the Agency’s
Central Data Exchange (CDX). Written
notification following renovator, dust
sampling technician, or lead-based paint
activities training courses can be
accomplished by using either the
sample form titled ‘‘Lead-Based Paint
Training Course Follow-up’’ or a similar
form containing the information
required in paragraph (c)(14)(ii) of this
section. All written notifications must
be delivered to EPA by U.S. Postal
Service, fax, commercial delivery
service, or hand delivery (persons
submitting notification by U.S. Postal
Service are reminded that they should
allow 3 additional business days for
delivery in order to ensure that EPA
receives the notification by the required
date). Instructions and sample forms can
be obtained from the NLIC at 1–800–
424–LEAD (5323), or on the Internet at
https://www.epa.gov/lead.
(d) Minimum training curriculum
requirements. To become accredited to
offer lead-based paint courses in the
specific disciplines listed in this
paragraph, training programs must
ensure that their courses of study
include, at a minimum, the following
course topics.
(1) Inspector. Instruction in the topics
described in paragraphs (d)(1)(iv), (v),
(vi), and (vii) of this section must be
included in the hands-on portion of the
course.
(i) Role and responsibilities of an
inspector.
(ii) Background information on lead
and its adverse health effects.
(iii) Background information on
Federal, State, and local regulations and
guidance that pertains to lead-based
paint and lead- based paint activities.
(iv) Lead-based paint inspection
methods, including selection of rooms
and components for sampling or testing.
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(v) Paint, dust, and soil sampling
methodologies.
(vi) Clearance standards and testing,
including random sampling.
(vii) Preparation of the final
inspection report.
(viii) Recordkeeping.
(2) Risk assessor. Instruction in the
topics described in paragraphs (d)(2)(iv),
(vi), and (vii) of this section must be
included in the hands-on portion of the
course.
(i) Role and responsibilities of a risk
assessor.
(ii) Collection of background
information to perform a risk
assessment.
(iii) Sources of environmental lead
contamination such as paint, surface
dust and soil, water, air, packaging, and
food.
(iv) Visual inspection for the purposes
of identifying potential sources of leadbased paint hazards.
(v) Lead hazard screen protocol.
(vi) Sampling for other sources of lead
exposure.
(vii) Interpretation of lead-based paint
and other lead sampling results,
including all applicable Federal or State
guidance or regulations pertaining to
lead-based paint hazards.
(viii) Development of hazard control
options, the role of interim controls, and
operations and maintenance activities to
reduce lead-based paint hazards.
(ix) Preparation of a final risk
assessment report.
(3) Supervisor. Instruction in the
topics described in paragraphs (d)(3)(v),
(vii), (viii), (ix), and (x) of this section
must be included in the hands-on
portion of the course.
(i) Role and responsibilities of a
supervisor.
(ii) Background information on lead
and its adverse health effects.
(iii) Background information on
Federal, State, and local regulations and
guidance that pertain to lead-based
paint abatement.
(iv) Liability and insurance issues
relating to lead-based paint abatement.
(v) Risk assessment and inspection
report interpretation.
(vi) Development and implementation
of an occupant protection plan and
abatement report.
(vii) Lead-based paint hazard
recognition and control.
(viii) Lead-based paint abatement and
lead-based paint hazard reduction
methods, including restricted practices.
(ix) Interior dust abatement/cleanup
or lead-based paint hazard control and
reduction methods.
(x) Soil and exterior dust abatement or
lead-based paint hazard control and
reduction methods.
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(xi) Clearance standards and testing.
(xii) Cleanup and waste disposal.
(xiii) Recordkeeping.
(4) Project designer. (i) Role and
responsibilities of a project designer.
(ii) Development and implementation
of an occupant protection plan for largescale abatement projects.
(iii) Lead-based paint abatement and
lead-based paint hazard reduction
methods, including restricted practices
for large-scale abatement projects.
(iv) Interior dust abatement/cleanup
or lead hazard control and reduction
methods for large-scale abatement
projects.
(v) Clearance standards and testing for
large scale abatement projects.
(vi) Integration of lead-based paint
abatement methods with modernization
and rehabilitation projects for large
scale abatement projects.
(5) Abatement worker. Instruction in
the topics described in paragraphs
(d)(5)(iv), (v), (vi), and (vii) of this
section must be included in the handson portion of the course.
(i) Role and responsibilities of an
abatement worker.
(ii) Background information on lead
and its adverse health effects.
(iii) Background information on
Federal, State and local regulations and
guidance that pertain to lead-based
paint abatement.
(iv) Lead-based paint hazard
recognition and control.
(v) Lead-based paint abatement and
lead-based paint hazard reduction
methods, including restricted practices.
(vi) Interior dust abatement methods/
cleanup or lead-based paint hazard
reduction.
(vii) Soil and exterior dust abatement
methods or lead-based paint hazard
reduction.
(6) Renovator. Instruction in the
topics described in paragraphs (d)(6)(iv),
(vi), (vii), and (viii) of this section must
be included in the hands-on portion of
the course.
(i) Role and responsibility of a
renovator.
(ii) Background information on lead
and its adverse health effects.
(iii) Background information on EPA,
HUD, OSHA, and other Federal, State,
and local regulations and guidance that
pertains to lead-based paint and
renovation activities.
(iv) Procedures for using acceptable
test kits to determine whether paint is
lead-based paint.
(v) Procedures for collecting a paint
chip sample and sending it to a
laboratory recognized by EPA under
section 405(b) of TSCA.
(vi) Renovation methods to minimize
the creation of dust and lead-based
paint hazards.
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(vii) Interior and exterior containment
and cleanup methods.
(viii) Methods to ensure that the
renovation has been properly
completed, including cleaning
verification and clearance testing.
(ix) Waste handling and disposal.
(x) Providing on-the-job training to
other workers.
(xi) Record preparation.
(7) Dust sampling technician.
Instruction in the topics described in
paragraphs (d)(6)(iv) and (vi) of this
section must be included in the handson portion of the course.
(i) Role and responsibility of a dust
sampling technician.
(ii) Background information on lead
and its adverse health effects.
(iii) Background information on
Federal, State, and local regulations and
guidance that pertains to lead-based
paint and renovation activities.
(iv) Dust sampling methodologies.
(v) Clearance standards and testing.
(vi) Report preparation.
(e) Requirements for the accreditation
of refresher training programs. A
training program may seek accreditation
to offer refresher training courses in any
of the following disciplines: Inspector,
risk assessor, supervisor, project
designer, abatement worker, renovator,
and dust sampling technician. To obtain
EPA accreditation to offer refresher
training, a training program must meet
the following minimum requirements:
(1) Each refresher course shall review
the curriculum topics of the full-length
courses listed under paragraph (d) of
this section, as appropriate. In addition,
to become accredited to offer refresher
training courses, training programs shall
ensure that their courses of study
include, at a minimum, the following:
(i) An overview of current safety
practices relating to lead-based paint in
general, as well as specific information
pertaining to the appropriate discipline.
(ii) Current laws and regulations
relating to lead-based paint in general,
as well as specific information
pertaining to the appropriate discipline.
(iii) Current technologies relating to
lead-based paint in general, as well as
specific information pertaining to the
appropriate discipline.
(2) Refresher courses for inspector,
risk assessor, supervisor, and abatement
worker must last a minimum of 8
training hours. Refresher courses for
project designer, renovator, and dust
sampling technician must last a
minimum of 4 training hours. Refresher
courses for all disciplines except project
designer must include a hands-on
component.
(3) Except for project designer
courses, for all other courses offered, the
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training program shall conduct a handson assessment, and at the completion of
the course, a course test.
(4) A training program may apply for
accreditation of a refresher course
concurrently with its application for
accreditation of the corresponding
training course as described in
paragraph (b) of this section. If so, EPA
shall use the approval procedure
described in paragraph (b) of this
section. In addition, the minimum
requirements contained in paragraphs
(c)(1) through (c)(5) and (c)(7) through
(c)(14), and (e)(1),through (e)(3) of this
section shall also apply.
(5) A training program seeking
accreditation to offer refresher training
courses only shall submit a written
application to EPA containing the
following information:
(i) The refresher training program’s
name, address, and telephone number.
(ii) A list of courses for which it is
applying for accreditation.
(iii) The name and documentation of
the qualifications of the training
program manager.
(iv) The name(s) and documentation
of the qualifications of the principal
instructor(s).
(v) A statement signed by the training
program manager certifying that the
refresher training program meets the
minimum requirements established in
paragraph (c) of this section, except for
the requirements in paragraph (c)(6) of
this section. If a training program uses
EPA-developed model training
materials, or training materials
approved by a State or Indian Tribe that
has been authorized by EPA under
§ 745.324 to develop its refresher
training course materials, the training
manager shall include a statement
certifying that, as well.
(vi) If the refresher training course
materials are not based on EPAdeveloped model training materials, the
training program’s application for
accreditation shall include:
(A) A copy of the student and
instructor manuals to be used for each
course.
(B) A copy of the course agenda for
each course.
(vii) All refresher training programs
shall include in their application for
accreditation the following:
(A) A description of the facilities and
equipment to be used for lecture and
hands-on training.
(B) A copy of the course test blueprint
for each course.
(C) A description of the activities and
procedures that will be used for
conducting the assessment of hands-on
skills for each course (if applicable).
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Federal Register / Vol. 76, No. 151 / Friday, August 5, 2011 / Rules and Regulations
(D) A copy of the quality control plan
as described in paragraph (c)(9) of this
section.
(viii) The requirements in paragraphs
(c)(1) through (c)(5), and (c)(7) through
(c)(14) of this section apply to refresher
training providers.
(ix) If a refresher training program
meets the requirements listed in this
paragraph, then EPA shall approve the
application for accreditation no more
than 180 days after receiving a complete
application from the refresher training
program. In the case of approval, a
certificate of accreditation shall be sent
to the applicant. In the case of
disapproval, a letter describing the
reasons for disapproval shall be sent to
the applicant. Prior to disapproval, EPA
may, at its discretion, work with the
applicant to address inadequacies in the
application for accreditation. EPA may
also request additional materials
retained by the refresher training
program under paragraph (i) of this
section. If a refresher training program’s
application is disapproved, the program
may reapply for accreditation at any
time.
(f) Re-accreditation of training
programs. (1) Unless re-accredited, a
training program’s accreditation,
including refresher training
accreditation, shall expire 4 years after
the date of issuance. If a training
program meets the requirements of this
section, the training program shall be
reaccredited.
(2) A training program seeking reaccreditation shall submit an
application to EPA no later than 180
days before its accreditation expires. If
a training program does not submit its
application for re-accreditation by that
date, EPA cannot guarantee that the
program will be re-accredited before the
end of the accreditation period.
(3) The training program’s application
for re-accreditation shall contain:
(i) The training program’s name,
address, and telephone number.
(ii) A list of courses for which it is
applying for re-accreditation.
(iii) The name and qualifications of
the training program manager.
(iv) The name(s) and qualifications of
the principal instructor(s).
(v) A description of any changes to
the training facility, equipment or
course materials since its last
application was approved that adversely
affects the students’ ability to learn.
(vi) A statement signed by the
program manager stating:
(A) That the training program
complies at all times with all
requirements in paragraphs (c) and (e) of
this section, as applicable; and
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(B) The recordkeeping and reporting
requirements of paragraph (i) of this
section shall be followed.
(vii) A payment of appropriate fees in
accordance with § 745.238.
(4) Upon request, the training program
shall allow EPA to audit the training
program to verify the contents of the
application for re-accreditation as
described in paragraph (f)(3) of this
section.
(g) Suspension, revocation, and
modification of accredited training
programs. (1) EPA may, after notice and
an opportunity for hearing, suspend,
revoke, or modify training program
accreditation, including refresher
training accreditation, if a training
program, training manager, or other
person with supervisory authority over
the training program has:
(i) Misrepresented the contents of a
training course to EPA and/or the
student population.
(ii) Failed to submit required
information or notifications in a timely
manner.
(iii) Failed to maintain required
records.
(iv) Falsified accreditation records,
instructor qualifications, or other
accreditation-related information or
documentation.
(v) Failed to comply with the training
standards and requirements in this
section.
(vi) Failed to comply with Federal,
State, or local lead-based paint statutes
or regulations.
(vii) Made false or misleading
statements to EPA in its application for
accreditation or re-accreditation which
EPA relied upon in approving the
application.
(2) In addition to an administrative or
judicial finding of violation, execution
of a consent agreement in settlement of
an enforcement action constitutes, for
purposes of this section, evidence of a
failure to comply with relevant statutes
or regulations.
(h) Procedures for suspension,
revocation or modification of training
program accreditation. (1) Prior to
taking action to suspend, revoke, or
modify the accreditation of a training
program, EPA shall notify the affected
entity in writing of the following:
(i) The legal and factual basis for the
suspension, revocation, or modification.
(ii) The anticipated commencement
date and duration of the suspension,
revocation, or modification.
(iii) Actions, if any, which the
affected entity may take to avoid
suspension, revocation, or modification,
or to receive accreditation in the future.
(iv) The opportunity and method for
requesting a hearing prior to final EPA
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action to suspend, revoke or modify
accreditation.
(v) Any additional information, as
appropriate, which EPA may provide.
(2) If a hearing is requested by the
accredited training program, EPA shall:
(i) Provide the affected entity an
opportunity to offer written statements
in response to EPA’s assertions of the
legal and factual basis for its proposed
action, and any other explanations,
comments, and arguments it deems
relevant to the proposed action.
(ii) Provide the affected entity such
other procedural opportunities as EPA
may deem appropriate to ensure a fair
and impartial hearing.
(iii) Appoint an official of EPA as
Presiding Officer to conduct the hearing.
No person shall serve as Presiding
Officer if he or she has had any prior
connection with the specific matter.
(3) The Presiding Officer appointed
pursuant to paragraph (h)(2) of this
section shall:
(i) Conduct a fair, orderly, and
impartial hearing within 90 days of the
request for a hearing.
(ii) Consider all relevant evidence,
explanation, comment, and argument
submitted.
(iii) Notify the affected entity in
writing within 90 days of completion of
the hearing of his or her decision and
order. Such an order is a final agency
action which may be subject to judicial
review.
(4) If EPA determines that the public
health, interest, or welfare warrants
immediate action to suspend the
accreditation of any training program
prior to the opportunity for a hearing, it
shall:
(i) Notify the affected entity of its
intent to immediately suspend training
program accreditation for the reasons
listed in paragraph (g)(1) of this section.
If a suspension, revocation, or
modification notice has not previously
been issued pursuant to paragraph (g)(1)
of this section, it shall be issued at the
same time the emergency suspension
notice is issued.
(ii) Notify the affected entity in
writing of the grounds for the immediate
suspension and why it is necessary to
suspend the entity’s accreditation before
an opportunity for a suspension,
revocation or modification hearing.
(iii) Notify the affected entity of the
anticipated commencement date and
duration of the immediate suspension.
(iv) Notify the affected entity of its
right to request a hearing on the
immediate suspension within 15 days of
the suspension taking place and the
procedures for the conduct of such a
hearing.
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(5) Any notice, decision, or order
issued by EPA under this section, any
transcripts or other verbatim record of
oral testimony, and any documents filed
by an accredited training program in a
hearing under this section shall be
available to the public, except as
otherwise provided by section 14 of
TSCA or by 40 CFR part 2. Any such
hearing at which oral testimony is
presented shall be open to the public,
except that the Presiding Officer may
exclude the public to the extent
necessary to allow presentation of
information which may be entitled to
confidential treatment under section 14
of TSCA or 40 CFR part 2.
(6) The public shall be notified of the
suspension, revocation, modification or
reinstatement of a training program’s
accreditation through appropriate
mechanisms.
(7) EPA shall maintain a list of parties
whose accreditation has been
suspended, revoked, modified or
reinstated.
(i) Training program recordkeeping
requirements. (1) Accredited training
programs shall maintain, and make
available to EPA, upon request, the
following records:
(i) All documents specified in
paragraph (c)(4) of this section that
demonstrate the qualifications listed in
paragraphs (c)(1) and (c)(2) of this
section of the training manager and
principal instructors.
(ii) Current curriculum/course
materials and documents reflecting any
changes made to these materials.
(iii) The course test blueprint.
(iv) Information regarding how the
hands-on assessment is conducted
including, but not limited to:
(A) Who conducts the assessment.
(B) How the skills are graded.
(C) What facilities are used.
(D) The pass/fail rate.
(v) The quality control plan as
described in paragraph (c)(9) of this
section.
(vi) Results of the students’ hands-on
skills assessments and course tests, and
a record of each student’s course
completion certificate.
(vii) Any other material not listed in
paragraphs (i)(1)(i) through (i)(1)(vi) of
this section that was submitted to EPA
as part of the program’s application for
accreditation.
(viii) For renovator refresher and dust
sampling technician refresher courses, a
copy of each trainee’s prior course
completion certificate showing that each
trainee was eligible to take the refresher
course.
(ix) For course modules delivered in
an electronic format, a record of each
student’s log-ins, launches, progress,
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and completion, and a copy of the
electronic learning completion
certificate for each student.
(2) The training program must retain
records pertaining to renovator, dust
sampling technician and lead-based
paint activities courses at the address
specified on the training program
accreditation application (or as
modified in accordance with paragraph
(i)(3) of this section) for the following
minimum periods:
(i) Records pertaining to lead-based
paint activities courses must be retained
for a minimum of 3 years and 6 months.
(ii) Records pertaining to renovator or
dust sampling technician courses
offered before April 22, 2010 must be
retained until July 1, 2015.
(iii) Records pertaining to renovator or
dust sampling technician courses
offered on or after April 22, 2010 must
be retained for a minimum of 5 years.
(3) The training program shall notify
EPA in writing within 30 days of
changing the address specified on its
training program accreditation
application or transferring the records
from that address.
(j) Amendment of accreditation. (1) A
training program must amend its
accreditation within 90 days of the date
a change occurs to information included
in the program’s most recent
application. If the training program fails
to amend its accreditation within 90
days of the date the change occurs, the
program may not provide renovator,
dust sampling technician, or lead-based
paint activities training until its
accreditation is amended.
(2) To amend an accreditation, a
training program must submit a
completed ‘‘Accreditation Application
for Training Providers,’’ signed by an
authorized agent of the training
provider, noting on the form that it is
submitted as an amendment and
indicating the information that has
changed.
(3) Training managers, principal
instructors, permanent training
locations. If the amendment includes a
new training program manager, any new
or additional principal instructor(s), or
any new permanent training location(s),
the training provider is not permitted to
provide training under the new training
manager or offer courses taught by any
new principal instructor(s) or at the new
training location(s) until EPA either
approves the amendment or 30 days
have elapsed, whichever occurs earlier.
Except:
(i) If the amendment includes a new
training program manager or new or
additional principal instructor that was
identified in a training provider
accreditation application that EPA has
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already approved under this section, the
training provider may begin to provide
training under the new training manager
or offer courses taught by the new
principal instructor on an interim basis
as soon as the provider submits the
amendment to EPA. The training
provider may continue to provide
training under the new training manager
or offer courses taught by the new
principal instructor if EPA approves the
amendment or if EPA does not
disapprove the amendment within 30
days.
(ii) If the amendment includes a new
permanent training location, the
training provider may begin to provide
training at the new permanent training
location on an interim basis as soon as
the provider submits the amendment to
EPA. The training provider may
continue to provide training at the new
permanent training location if EPA
approves the amendment or if EPA does
not disapprove the amendment within
30 days.
9. In § 745.238, add paragraph (c)(5) to
read as follows:
■
§ 745.238 Fees for accreditation and
certification of lead-based paint activities.
*
*
*
*
*
(c) * * *
(5) Accreditation amendment fees. No
fee will be charged for accreditation
amendments.
*
*
*
*
*
■ 10. In § 745.326, revise paragraphs
(a)(2)(i), (a)(2)(ii), (d), (e)(1), and (e)(3) to
read as follows:
§ 745.326 Renovation: State and Tribal
program requirements.
(a) * * *
(2) * * *
(i) Procedures and requirements for
the accreditation of renovation and dust
sampling technician training programs.
A State and Tribal program is not
required to include procedures and
requirements for the dust sampling
technician training discipline if the
State or Tribal program requires dust
sampling to be performed by a certified
lead-based paint inspector or risk
assessor.
(ii) Procedures and requirements for
accredited initial and refresher training
for renovators and dust sampling
technicians and on-the-job training for
other individuals who perform
renovations.
*
*
*
*
*
(d) Certification of individuals and/or
renovation firms. To be considered at
least as protective as the Federal
program, the State or Tribal program
must:
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(1) Establish procedures and
requirements that ensure that
individuals who perform or direct
renovations are properly trained. These
procedures and requirements must
include:
(i) A requirement that renovations be
performed and directed by at least one
individual who has been trained by an
accredited training program.
(ii) Procedures and requirements for
accredited refresher training for these
individuals.
(iii) Procedures and requirements for
individuals who have received
accredited training to provide on-the-job
training for those individuals who
perform renovations but do not receive
accredited training. A State and Tribal
program is not required to include
procedures and requirements for on-thejob training for renovation workers if the
State or Tribal program requires
accredited initial and refresher training
for all persons who perform
renovations.
(2) Establish procedures and
requirements for the formal certification
and re-certification of renovation firms.
(3) Establish procedures for the
suspension, revocation, or modification
of certifications.
(e) * * *
(1) Renovations must be conducted
only by certified renovation firms, using
trained individuals.
*
*
*
*
*
(3) Certified individuals and/or
renovation firms must retain
appropriate records.
*
*
*
*
*
■ 11. In § 745.327, revise paragraphs
(b)(1), (b)(2), (b)(3), and (c)(2) to read as
follows:
§ 745.327 State or Indian Tribal lead-based
paint compliance and enforcement
programs.
*
*
*
*
(b) * * *
(1) Lead-based paint activities or
renovation requirements. State or Tribal
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*
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lead-based paint compliance and
enforcement programs will be
considered adequate if the State or
Indian Tribe demonstrates, in its
application at § 745.324(b)(2), that it has
established a lead-based paint program
that contains all of the elements
specified in § 745.325 or § 745.326, or
both, as applicable.
(2) Authority to enter. State or Tribal
officials must be able to enter, through
consent, warrant, or other authority,
premises or facilities where lead-based
paint violations may occur for purposes
of conducting inspections.
(i) State or Tribal officials must be
able to enter premises or facilities where
those engaged in training for lead-based
paint activities or renovations conduct
business.
(ii) For the purposes of enforcing a
renovation program, State or Tribal
officials must be able to enter a firm’s
place of business or work site.
(iii) State or Tribal officials must have
authority to take samples and review
records as part of the lead-based paint
inspection process.
(3) Flexible remedies. A State or
Tribal lead-based paint compliance and
enforcement program must provide for a
diverse and flexible array of
enforcement statutory and regulatory
authorities and remedies. At a
minimum, these authorities and
remedies, which must also be reflected
in an enforcement response policy, must
include the following:
(i) The authority to issue warning
letters, Notices of Noncompliance,
Notices of Violation, or the equivalent;
(ii) The authority to assess
administrative or civil fines, including a
maximum penalty authority for any
violation in an amount no less than
$5,000 per violation per day;
(iii) The authority to assess the
maximum penalties or fines for each
instance of violation and, if the
violation is continuous, the authority to
assess penalties or fines up to the
maximum amount for each day of
violation, with all penalties assessed or
PO 00000
Frm 00030
Fmt 4701
Sfmt 9990
collected being appropriate for the
violation after consideration of factors
as the State or Tribe determine to be
relevant, including the size or viability
of the business, enforcement history,
risks to human health or the
environment posed by the violation, and
other similar factors;
(iv) The authority to commence an
administrative proceeding or to sue in
courts of competent jurisdiction to
recover penalties;
(v) The authority to suspend, revoke,
or modify the accreditation of any
training provider or the certification of
any individual or firm;
(vi) The authority to commence an
administrative proceeding or to sue in
courts of competent jurisdiction to
enjoin any threatened or continuing
violation of any program requirement,
without the necessity of a prior
suspension or revocation of a trainer’s
accreditation or a firm’s or individual’s
certification;
(vii) The authority to apply criminal
sanctions, including recovering fines;
and
(viii) The authority to enforce its
authorized program using a burden of
proof standard, including the degree of
knowledge or intent of the respondent
that is no greater than it is for EPA
under TSCA.
*
*
*
*
*
(c) * * *
(2) Compliance assistance. A State or
Tribal lead-based paint compliance and
enforcement program must provide
compliance assistance to the public and
the regulated community to facilitate
awareness and understanding of and
compliance with State or Tribal
requirements governing the conduct of
lead-based paint activities or
renovations. The type and nature of this
assistance can be defined by the State or
Indian Tribe to achieve this goal.
*
*
*
*
*
[FR Doc. 2011–19417 Filed 8–4–11; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\05AUR4.SGM
05AUR4
Agencies
[Federal Register Volume 76, Number 151 (Friday, August 5, 2011)]
[Rules and Regulations]
[Pages 47918-47946]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-19417]
[[Page 47917]]
Vol. 76
Friday,
No. 151
August 5, 2011
Part IV
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 745
Lead; Clearance and Clearance Testing Requirements for the Renovation,
Repair, and Painting Program; Final Rule
Federal Register / Vol. 76, No. 151 / Friday, August 5, 2011 / Rules
and Regulations
[[Page 47918]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 745
[EPA-HQ-OPPT-2005-0049; FRL-8881-8]
RIN 2070-AJ57
Lead; Clearance and Clearance Testing Requirements for the
Renovation, Repair, and Painting Program
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: As part of a settlement of litigation over certain post-
renovation cleaning requirements of the 2008 Lead Renovation, Repair,
and Painting Program (RRP) rule, the EPA agreed to propose a number of
revisions to the 2008 RRP rule that established accreditation,
training, certification, and recordkeeping requirements as well as work
practice standards for persons performing renovations for compensation
in most pre-1978 housing and child-occupied facilities and to
subsequently take final action on the proposed rule by July 15, 2011.
The proposed rule published on May 6, 2010. EPA has decided not to
promulgate dust wipe testing and clearance requirements as proposed.
However, EPA is promulgating several other revisions to the RRP rule,
including a provision allowing a certified renovator to collect a paint
chip sample and send it to a recognized laboratory for analysis in lieu
of using a lead test kit, minor changes to the training program
accreditation application process, standards for e-learning in
accredited training programs, minimum enforcement provisions for
authorized state and tribal renovation programs, and minor revisions to
the training and certification requirements for renovators. EPA is also
promulgating clarifications to the requirements for vertical
containment on exterior renovation projects, the prohibited or
restricted work practice provisions, and the requirements for high-
efficiency particulate air (HEPA) vacuums. Today's action is EPA's
final action on all aspects of the May 6, 2010 proposal.
DATES: This final rule is effective October 4, 2011.
ADDRESSES: EPA has established a docket for this action under docket
identification (ID) number EPA-HQ-OPPT-2005-0049. All documents in the
docket are listed in the docket index available at https://www.regulations.gov. Although listed in the index, some information is
not publicly available, e.g., Confidential Business Information (CBI)
or other information whose disclosure is restricted by statute. Certain
other material, such as copyrighted material, is not placed on the
Internet and will be publicly available only in hard copy. Publicly
available docket materials are available in the electronic docket at
https://www.regulations.gov, or, if only available in hard copy, at the
OPPT Docket. The OPPT Docket is located in the EPA Docket Center (EPA/
DC) at Rm. 3334, EPA West Bldg., 1301 Constitution Ave., NW.,
Washington, DC. The EPA/DC Public Reading Room hours of operation are
8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal
holidays. The telephone number of the EPA/DC Public Reading Room is
(202) 566-1744, and the telephone number for the OPPT Docket is (202)
566-0280. Hearing- or speech-impaired persons may reach the above
telephone numbers through TTY by calling the toll-free Federal Relay
Service at 1-800-877-8339. Docket visitors are required to show
photographic identification, pass through a metal detector, and sign
the EPA visitor log. All visitor bags are processed through an X-ray
machine and subject to search. Visitors will be provided an EPA/DC
badge that must be visible at all times in the building and returned
upon departure.
FOR FURTHER INFORMATION CONTACT: For technical information contact:
Cindy Wheeler, National Program Chemicals Division (7404T), Office of
Pollution Prevention and Toxics, Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone number:
(202) 566-0484; e-mail address: wheeler.cindy@epa.gov.
For general information contact: The TSCA-Hotline, ABVI-Goodwill,
422 South Clinton Ave., Rochester, NY 14620; telephone number: (202)
554-1404; e-mail address: TSCA-Hotline@epa.gov. Hearing- or speech-
impaired persons may reach the above telephone number through TTY by
calling the toll-free Federal Relay Service at 1-800-877-8339.
SUPPLEMENTARY INFORMATION:
I. Does this action apply to me?
You may be potentially affected by this action if you perform
renovations of target housing or child-occupied facilities for
compensation, dust sampling, or dust testing. You may also be affected
by this action if you perform lead-based paint inspections, lead hazard
screens, risk assessments or abatements in target housing or child-
occupied facilities or if you operate a training program for
individuals who perform any of these activities. ``Target housing'' is
defined in section 401 of TSCA as any housing constructed prior to
1978, except housing for the elderly or persons with disabilities
(unless any child under age 6 resides or is expected to reside in such
housing) or any 0-bedroom dwelling. Under this rule, a child-occupied
facility is a building, or a portion of a building, constructed prior
to 1978, visited regularly by the same child, under 6 years of age, on
at least 2 different days within any week (Sunday through Saturday
period), provided that each day's visit lasts at least 3 hours and the
combined weekly visits last at least 6 hours, and the combined annual
visits last at least 60 hours.
Potentially-affected entities may include, but are not limited to:
Building construction (NAICS code 236), e.g., single
family housing construction, multi-family housing construction,
residential remodelers.
Specialty trade contractors (NAICS code 238), e.g.,
plumbing, heating, and air-conditioning contractors, painting and wall
covering contractors, electrical contractors, finish carpentry
contractors, drywall and insulation contractors, siding contractors,
tile and terrazzo contractors, glass and glazing contractors.
Real estate (NAICS code 531), e.g., lessors of residential
buildings and dwellings, residential property managers.
Child day care services (NAICS code 624410).
Elementary and secondary schools (NAICS code 611110),
e.g., elementary schools with kindergarten classrooms.
Other technical and trade schools (NAICS code 611519),
e.g., training providers.
Engineering services (NAICS code 541330) and building
inspection services (NAICS code 541350), e.g., dust sampling
technicians.
Lead abatement professionals (NAICS code 562910), e.g.,
firms and supervisors engaged in lead-based paint activities.
This listing is not intended to be exhaustive, but rather provides
a guide for readers regarding entities likely to be affected by this
action. Other types of entities not listed in this unit could also be
affected. The North American Industrial Classification System (NAICS)
codes have been provided to assist you and others in determining
whether this action might apply to certain entities. If you have any
questions regarding the applicability of this action to a particular
entity, consult
[[Page 47919]]
the technical person listed under FOR FURTHER INFORMATION CONTACT.
II. Background
A. What action is the agency taking?
On May 6, 2010, EPA proposed a number of revisions to the 2008 Lead
Renovation, Repair, and Painting Program (RRP) rule that established
accreditation, training, certification, and recordkeeping requirements
as well as work practice standards for persons performing renovations
for compensation in most pre-1978 housing and child-occupied facilities
(Ref. 1). Specifically, EPA proposed requirements for dust wipe
testing, clearance, allowing a certified renovator to collect a paint
chip sample and send it to a recognized laboratory for analysis, minor
changes to the training program accreditation application process,
standards for e-learning in accredited training programs, minimum
enforcement provisions for authorized state and tribal renovation
programs, and minor revisions to the training and certification
requirements for renovators. EPA has decided not to promulgate dust
wipe testing and clearance requirements as proposed. However, EPA is
promulgating several of the other proposed revisions to the RRP rule,
including a provision allowing a certified renovator to collect a paint
chip sample and send it to a recognized laboratory for analysis in lieu
of using a lead test kit, minor changes to the training program
accreditation application process, standards for e-learning in
accredited training programs, minimum enforcement provisions for
authorized state and tribal renovation programs, and minor revisions to
the training and certification requirements for renovators. EPA is also
promulgating clarifications to the requirements for vertical
containment on exterior renovation projects, the prohibited or
restricted work practice provisions, and the requirements for high-
efficiency particulate air (HEPA) vacuums. Today's action is EPA's
final action on all aspects of the May 6, 2010 proposal.
B. What is the agency's authority for taking this action?
These work practice, training, certification and accreditation
requirements, and the State, Territorial and Tribal authorization
provisions are being promulgated under the authority of sections
402(c)(3), 404, and 407 of the Toxic Substances Control Act (TSCA), 15
U.S.C. 2682(c)(3), 2684, and 2687.
C. What are the specific provisions of this action?
1. Clearance and dust wipe testing requirements for renovations. As
discussed in this unit, EPA has decided not to promulgate clearance and
dust wipe testing requirements as proposed in May 2010 for certain
renovations covered by the 2008 Lead Renovation, Repair, and Painting
(RRP) rule (Ref. 2).
a. Background. In promulgating the final 2008 RRP rule, EPA
determined that renovation, repair, and painting activities, when
performed in the presence of lead-based paint, create lead-based paint
hazards. Section 402(c)(3) of TSCA directs EPA to revise its
regulations governing lead-based paint inspections, risk assessments,
and abatements (the Lead-based Paint Activities Regulations, or
abatement regulations, Ref. 3) to apply to renovation and remodeling
activities that create lead-based paint hazards. Accordingly, the 2008
RRP rule established accreditation, training, certification, and
recordkeeping requirements as well as work practice standards for
persons performing renovations for compensation in most pre-1978
housing and child-occupied facilities. Among other things, the work
practice standards require renovation firms to follow specific
requirements for containing the work area, refrain from using certain
high-dust-generating work practices, and follow a specific cleaning
protocol, including a step called ``cleaning verification,'' after
concluding the paint-disturbing tasks involved in a renovation.
As discussed in the preamble to the 2010 proposal, EPA is
particularly concerned about dust-lead hazards generated by renovations
because of the well-documented toxicity of lead, especially to younger
children. For a more detailed discussion of the health effects of lead
exposure, refer to information in the 2010 proposal (Ref. 1) and the
2008 RRP final rule (Ref. 2).
One of the more difficult issues in the 2008 RRP rulemaking was the
issue of determining when a renovation work area has been properly
cleaned and is ready for reoccupancy. After a lead-based paint
abatement project, EPA's Lead-Based Paint Activities Regulations
require the abatement contractor to achieve clearance. This means that
the contractor must demonstrate, through dust wipe testing, that dust
lead levels remaining in the abatement work area are below the
clearance levels established in the 2001 rulemaking entitled
``Identification of Dangerous Levels of Lead'' under section 403 of the
Toxic Substances Control Act (Ref. 4). Dust wipe samples for clearance
purposes must be collected by a certified individual and analyzed by an
entity recognized under the National Lead Laboratory Accreditation
Program (NLLAP).
When promulgating the 2008 RRP rule, EPA considered requiring a
similar process after renovations, but for various reasons, did not do
so. EPA did not interpret its statutory mandate under TSCA section
402(c)(3) as simply expanding the scope of the Lead-based Paint
Activities Regulations to also cover renovation activities. Rather, EPA
stated, in the final 2008 RRP rule, its belief that Congress intended
for EPA to make revisions to those existing regulations to adapt them
to a different set of activities and a very different regulated
community. In establishing the cleaning element of the work practice
requirements for renovations, EPA primarily relied on the results of
two studies, the ``Electrostatic Cloth and Wet Cloth Field Study in
Residential Housing'' (Ref. 5) and the ``Characterization of Dust Lead
Levels after Renovation, Repair, and Painting Activities'' (the ``Dust
Study,'' Ref. 6) to determine that the full suite of RRP work practice
requirements, including containment, cleaning, and cleaning
verification, was effective at minimizing exposure to lead-based paint
hazards created by renovation, repair, and painting activities.
EPA also considered various other factors as well as issues raised
by commenters. Among these were the differences between abatement and
renovation, the costs of dust wipe testing and clearance, the potential
delay in obtaining results, and the likelihood that renovation firms
would become liable for pre-existing dust-lead hazards. Abatements have
only one purpose, to permanently eliminate lead-based paint or lead-
based paint hazards, while renovations are performed for many reasons
that often have nothing to do with lead-based paint. Concerns about the
costs of dust wipe testing and clearance were brought to EPA's
attention during stakeholder input opportunities provided by EPA before
the proposed RRP rule was issued in 2006 and echoed by commenters on
the 2006 proposed RRP rule. If EPA had required dust wipe testing and
clearance after every renovation project, it would have made up a
significant portion of the cost of smaller projects. In addition, dust
wipe testing results may not be available for several days. If EPA had
required traditional abatement-style clearance after renovations, the
work area would not be able to be re-occupied while waiting for the
laboratory results.
[[Page 47920]]
Commenters also noted that requiring clearance after renovation jobs
could, in some instances, result in the renovation firm being held
responsible for abating all dust-lead hazards, including such hazards
that may have existed in the area before the renovation commenced.
Other commenters on the 2006 proposed RRP rule thought that
renovation work areas ought to be tested and cleared for re-occupancy
in the same way that abatement work areas are cleared through the
clearance process, including dust wipe testing. Many commenters
believed that renovation firms should be required to demonstrate that
no dust-lead hazards had been left behind in the work area. These
commenters contended that the only effective way to do this is through
dust wipe testing and clearance. While EPA understood the issues raised
by these commenters, and agreed with some of the points that they made,
EPA remained convinced that the suite of RRP work practices would be
practical for renovation firms to implement while effectively
minimizing exposure to dust-lead hazards created by renovations. The
RRP work practices are, in essence, requirements to ensure that
renovators undertake traditional renovation activities--e.g., removal
or modification of existing surfaces, containment and cleanup of dust
and debris, and ensuring the job site is cleaned up--in a lead-safe
way. EPA believes the RRP rule effectively minimizes exposure to
hazards generated by renovation activities without imposing practices
and disciplines that are outside the scope of traditional renovation
activities. More information on the comments received and EPA's
decisions can be found in the preamble to the final 2008 RRP rule (Ref.
2).
b. 2010 Proposal. Based on additional stakeholder input received
after the final rule was issued, and an August 2009 agreement entered
into with several environmental and children's health advocacy groups
in settlement of their lawsuit challenging the final 2008 RRP rule, EPA
agreed to consider whether some of the decisions made in 2008 with
regard to dust wipe testing and clearance should be modified.
Accordingly, on May 6, 2010, EPA proposed to require dust wipe
testing after many renovations covered by the RRP rule (Ref. 1). Under
the 2010 proposal, dust wipe testing would have been required on
uncarpeted floors, windowsills, and window troughs in the work area
after the following types of interior renovations:
Use of a heat gun at temperatures below 1100 degrees
Fahrenheit.
Removal or replacement of window or door frames.
Scraping 60 ft\2\ or more of painted surfaces.
Removing more than 40 ft\2\ of trim, molding, cabinets, or
other fixtures.
After these renovations, the renovation firm would have been
required to collect dust wipe samples and have them analyzed for lead
content by an entity recognized under NLLAP. The renovation firm would
then have been required to provide these results to the owners and
occupants of the renovated property.
For another subset of jobs involving demolition or removal of
plaster through destructive means or the disturbance of paint using
machines designed to remove paint through high-speed operation, such as
power sanders or abrasive blasters, EPA proposed to require the
renovation firm to achieve clearance. This would have involved a
demonstration, through dust wipe testing, that dust-lead levels
remaining on uncarpeted floors, windowsills, and window troughs in the
work area were below regulatory clearance levels. These clearance
levels would have been identical to the clearance levels established
for the lead-based paint abatement program, which are codified at 40
CFR 745.227(e)(8)(viii), i.e., 40 [mu]g/ft\2\ on floors, 250 [mu]g/
ft\2\ on interior windowsills, and 400 [mu]g/ft\2\ on window troughs,
based on wipe samples. These additional requirements in the 2010
proposal were designed to ensure that lead-based paint hazards
generated by renovation work are adequately cleaned after renovation
work is finished and before the work areas are re-occupied.
c. This final rule. Maintaining the distinction between abatement
and renovation activities has been an important issue throughout the
rulemaking process for the 2008 RRP rule. As discussed in the preamble
to the 2008 RRP rule, abatements and renovations are performed by
different contractors for different purposes, although similar
activities, such as window replacements, may be involved. Typically,
when an abatement is performed, the housing is either unoccupied or the
occupants are temporarily relocated to lead-safe housing until the
abatement has been demonstrated to have been properly completed through
the clearance process. Carpet in the housing is usually removed as part
of the abatement because it is difficult to demonstrate that it is free
of lead-based paint hazards. Uncarpeted floors that have not been
replaced during the abatement may need to be refinished or sealed in
order to achieve clearance. Abatements have only one purpose--to
permanently eliminate lead-based paint and lead-based paint hazards. In
contrast, renovations other than interim controls are performed for
reasons unrelated to lead-based paint or lead-based paint hazards.
Renovations may be performed while the property is occupied or
unoccupied, but occupants do not typically relocate pending the
completion of the project.
EPA did not design or intend the RRP rule to address cleanup of
pre-existing dust-lead hazards. While the cleaning requirements of the
RRP rule will, in some cases, have the ancillary benefit of removing
some pre-existing dust-lead hazards, the cleaning requirements were
designed to effectively clean-up lead-based paint hazards created
during renovation activities without changing the scope of the
renovation activity itself. Accordingly, the RRP rule does not require
cleaning of dust or any other possible lead sources in portions of
target housing or child-occupied facilities beyond locations in and
around the work area. Nor does the RRP rule require the replacement of
carpets in the area of the renovation or the refinishing or sealing of
uncarpeted floors. The approach in the RRP rule was designed to address
the lead-based paint hazards created during the renovation while not
requiring renovation firms to remediate or eliminate hazards beyond the
scope of the work they were hired to do.
In addition, EPA has interpreted practicality in implementation to
be an element of the statutory directive to take into account
effectiveness and reliability. As discussed in the preamble to the
final 2008 RRP rule, EPA believes that, given the highly variable
nature of the regulated community, the work practices required by the
RRP rule should be simple to understand and easy to use. EPA is
cognizant of the fact that the RRP rule applies to a range of
individuals from day laborers to property maintenance staff to master
craftsmen performing a range of activities from simple drywall repair
to window replacement to complete kitchen and bath renovations to
building additions and everything in between. Work practices that are
easy and practical to use are more likely to be followed by all of the
persons who perform renovations, and, therefore, more likely to be
reliable and effective in minimizing exposure to lead-based paint
hazards created by renovation activities.
The 2010 proposal for this rule was EPA's attempt to explore
whether clearance and dust wipe testing requirements should be added to
the
[[Page 47921]]
RRP rule to provide additional protection for some renovations. EPA's
intention was to do this without generally holding renovation firms
responsible for abating pre-existing dust-lead hazards or creating
requirements that would impair the overall reliability and
effectiveness of the work practice requirements.
EPA received over 300 comments on its 2010 proposal. Members of the
regulated community and other industry commenters were generally
concerned that EPA had upset the balance it had struck in the 2008 RRP
rule, arguing that a dust wipe testing or clearance requirement would
have the effect of holding renovation firms responsible for pre-
existing hazards, whether directly by regulation, in the case of the
proposed clearance requirements, or indirectly by requiring firms to
provide information on post-renovation dust lead levels to the property
owner and occupant. While there was little support for dust wipe
testing alone, commenters that supported the 2010 proposal generally
thought that a clearance requirement should be imposed and expanded to
most, if not all, renovations.
After carefully weighing the issues at stake and considering the
concerns raised by commenters, and as explained in greater detail
below, EPA has concluded that, on balance, the information before the
Agency does not support imposing a dust wipe testing or clearance
requirement on renovations. In particular, EPA is convinced that the
work practices established in the 2008 RRP rule are reliable,
effective, and safe, and that imposing a dust wipe testing or clearance
requirement is unwarranted.
Almost all of the commenters were opposed to the proposed
provisions requiring only dust wipe testing after certain renovations.
Members of the regulated community and other industry commenters argued
that a dust wipe testing requirement would have the effect of holding
renovation firms responsible for pre-existing hazards, albeit
indirectly, by requiring firms to provide information on post-
renovation dust lead levels to the property owner and occupant. This
requirement would also have the effect of adding an element that is not
generally considered a renovation activity, i.e., taking samples for
laboratory analysis, and indeed, would have to be performed by a third
party or only after a renovator received training in a separate and
distinct discipline--either as a dust wipe sample technician or a lead-
based paint inspector. In addition, many argued that the Dust Study
generally shows that the RRP work practices are effective at minimizing
occupant exposure to dust-lead hazards created by renovations, so
additional dust wipe testing or clearance requirements are unnecessary.
These commenters noted that this is particularly true for the
renovations for which EPA proposed to require only dust wipe testing,
because those renovations were specifically tested in the Dust Study.
In addition, commenters suggested that the categories of jobs for which
dust wipe testing or clearance would be required were arbitrary and not
based on sufficient evidence.
Some commenters, including several states, also questioned the
utility and value of dust wipe testing in the absence of a clearance
requirement. Some were concerned that property owners and occupants
would not understand the significance of the results of dust wipe
samples that exceed the clearance standards or what steps they should
take to protect themselves and their families. One argued that, in the
absence of standards and required remedial actions, dust wipe testing
would add expense and time to a renovation project without providing a
concrete increase in protection for occupants. On the other hand, other
commenters contended that the feedback provided by numerical dust wipe
testing results would result in improved cleaning performance on the
part of renovation firms. Some cited anecdotal evidence of poor
contractor performance in other programs, such as the abatement
program, in support of a contention that the RRP rule work practices
would not be as effective at minimizing dust-lead hazards as they were
in the Dust Study.
Additionally, after considering previous interpretations of the
statutory requirements and the comments received on this specific
issue, EPA is not convinced that dust wipe testing in the absence of a
clearance requirement would be a safe, reliable and effective work
practice within the meaning of TSCA Section 402. As commenters noted,
provision of dust wipe testing results in the absence of a clearance
requirement does not by itself reduce the amount of dust generated
during or left behind following a renovation. Furthermore, dust wipe
testing results alone are not part of the information that must be
provided at the pre-renovation stage under Section 406(b) of TSCA, and
providing this type of information is not typically considered a
renovation work practice. Again, the dust wipe testing would either
have to be done by a third party or by a renovator who has taken a
course and been trained in a completely different discipline.
EPA believes these commenters raise valid considerations. In
particular, EPA agrees that the Dust Study demonstrates that with
respect to these very activities, the suite of RRP work practices
reliably addressed the hazards created by the renovation. In addition,
although EPA attempted in its 2010 proposal to distinguish renovation
activities that it thought warranted the addition of a dust wipe
testing requirement from those that did not (and from those that
warranted imposition of a clearance requirement), EPA acknowledges that
its 2010 proposal lacked a strong basis for drawing these lines--a
point made by many commenters. While some commenters urged the point
that dust wipe testing would encourage better cleanup, and provided
anecdotal support for that view, EPA has no record basis to judge the
likelihood or frequency of this potential impact. This logic could
potentially lead to requiring dust wipe testing for all jobs--a
significant change in the existing rule that EPA is not prepared to
make without better supporting evidence. Accordingly, upon the
information before it, the Agency does not believe that a dust testing
requirement alone is warranted. EPA notes that homeowners can arrange
to have dust wipe testing done as part of a renovation (or at any time)
if they would like information about dust-lead levels in their homes.
EPA also notes that property owners can contractually elect clearance
testing at the completion of a project. EPA's Web site has a page
homeowners can use to locate certified lead inspection and abatement
professionals and accredited training providers in their state (https://www.epa.gov/lead/pubs/locate.htm).
EPA also proposed to require that renovation firms achieve
clearance for a subset of jobs involving demolition or removal of
plaster through destructive means or the disturbance of paint using
machines designed to remove paint through high-speed operation, such as
power sanders or abrasive blasters. Nonetheless, EPA remained concerned
about promulgating a requirement that could make renovation firms
responsible for pre-existing conditions and fundamentally change the
scope of the renovation activity itself. Therefore, to avoid making
renovation firms replace carpets or refinish floors when they were not
hired to do so, EPA proposed to allow a renovation firm to stop after
two failed dust wipe tests on a particular surface if the firm was not
hired to refinish or replace that surface.
EPA was particularly concerned about these types of jobs because it
had evidence that the work practices were not effective when machines
designed
[[Page 47922]]
to remove paint through high speed operation were operated without HEPA
shrouds and created large quantities of dust. EPA was concerned that
even if such machines were equipped with HEPA shrouds, the RRP work
practices may not be effective at minimizing exposure to lead hazards
created by the renovation. Additionally, EPA stated its belief that
dust created by the demolition or removal of plaster was similarly
difficult to clean and therefore the RRP work practices might not be
effective at minimizing exposure to lead hazards created by the
renovation.
With respect to the proposed clearance requirements, commenters
generally fell into two camps. Commenters who were in ``favor'' of the
2010 proposal nonetheless generally argued that the proposed clearance
requirements should be expanded to cover most if not all renovation
activities because clearance is the only method to ensure that no lead
hazards remain upon the completion of a renovation job. Commenters who
opposed any type of clearance requirement argued again that it erased
the distinction between renovations and abatements and made renovation
firms responsible for pre-existing conditions. These commenters also
questioned the relevance of the studies EPA cited in support of its
2010 proposal to require clearance after renovations involving
demolition or removal of plaster through destructive means or the
disturbance of paint using machines designed to remove paint through
high-speed operation. The cited studies include EPA's Environmental
Field Sampling Study (EFSS, Ref. 7) and studies examining the
effectiveness of HEPA exhaust control on power tools (Ref. 8). Many of
the HEPA exhaust control studies addressed dusts not typically created
during renovations regulated by the RRP rule, such as crystalline
silica dust resulting from the grinding of concrete. Others addressed
surfaces and surface coatings not typically encountered during
renovations covered by the RRP rule; one involved paint removal from
automobiles. Notwithstanding EPA's 2010 proposal and requests for
comment, EPA did not receive any additional information or data with
respect to the dust or hazards created by these activities. Finally, on
both sides of the issue, commenters did not favor the proposed
provision allowing renovation firms to stop after two failed dust wipe
tests, and, although some alternative suggestions were offered, none
effectively addressed the competing considerations of occupant
protection and not expanding the scope of the renovation work.
EPA recognizes that imposing a clearance requirement would be a
departure from the balance struck in the RRP rule with respect to the
distinction between abatement and renovations. Accordingly, in EPA's
judgment, the Agency should be in a position to conclude with a fair
amount of certainty that doing so was necessary in light of its
obligation to promulgate work practices that take into account
reliability, effectiveness, and safety. Here, EPA acknowledges that it
does not have data to support its concern that dust created by
destructive demolition of plaster may be similar in nature to dust
generated by machines designed to remove paint through high speed
operation, and thus would have the potential to overwhelm the RRP
cleaning protocol. EPA also recognizes that the data on the efficiency
of HEPA is only suggestive that there might be an issue concerning
these practices. Again, the studies EPA reviewed suggested that HEPA
exhaust control could reduce the airborne dust levels by 90-95%. As
commenters pointed out, it is not clear the results of these studies
are applicable to the home renovation setting, given the differences
between the surfaces and paints in residential settings and the
surfaces and paints involved in the studies. Even if the results were
applicable, there is no direct evidence that the RRP lead safe work
practices could not reliably address the dust hazards created by the
use of such power tools. Having received no additional information in
this regard, EPA has determined that, among other things, the available
information does not support a clearance requirement. Nevertheless, as
discussed further in Unit II.C.7. of this preamble, EPA is adding a
requirement that power tools be operated so that no visible dust or
release of air occurs outside of the shroud or containment system. This
requirement will work to mitigate the concerns EPA had with respect to
the efficiency of power tool dust collection systems and the
possibility that such tools might overwhelm the containment and
specialized cleaning protocols of the RRP work practices.
In an effort to ensure that the proposed clearance requirement
would not typically result in holding renovation firms responsible for
abating pre-existing dust-lead hazards, EPA included a provision to
allow firms to stop the clearance procedure after two failed clearance
tests on a particular surface unless they had also contracted to
refinish the surface. Upon further reflection, EPA is concerned about
the potential ineffectiveness of this effort, because it would likely
still result in some renovation firms having to clean up pre-existing
dust-lead hazards. At the same time, the proposed provision would not
result in the certainty regarding elimination of dust-lead hazards that
is the defining characteristic of a clearance requirement. In addition,
the practical effect of such a provision is that the proposed clearance
requirement would, in fact, often result in a dust wipe testing
requirement. As such, it raises many of the same issues and concerns
that ultimately persuaded EPA not to promulgate just dust wipe testing
requirements.
Furthermore, as stated above, EPA does not believe the record
before it strongly supports the line-drawing in its 2010 proposal,
which would have resulted in a clearance requirement for some
renovations, a dust wipe testing requirement for others, and no testing
for the rest of the renovations covered by the RRP rule.
In revising the abatement regulations to apply to renovations, EPA
has sought to keep the renovation requirements relatively simple and
easy to apply, while attaining the overall objective of minimizing
exposure to dust-lead hazards generated by renovation activities. EPA
is concerned that the proposed three-tier system would add a level of
complexity to the rule that is undesirable. While EPA could potentially
draw different lines in this final rule, or promulgate a requirement
that all jobs achieve clearance, EPA does not believe it has a strong
basis to do so.
The combination of these factors has convinced EPA that imposing a
clearance requirement is unwarranted. The best evidence that EPA has of
the effectiveness of the work practice standards is the Dust Study, and
it demonstrates that overall the full suite of RRP work practices is
effective at minimizing exposure to dust-lead hazards created by
renovations. Without more, EPA is unable to conclude that the RRP work
practice promulgated in 2008 should be significantly altered.
Additionally, a variety of commenters, including industry
representatives and some states, suggested that EPA had issued its 2010
proposal to require dust wipe testing and clearance too soon after
promulgation of the 2008 RRP rule. At the time that the 2010 proposal
was issued, full implementation of the 2008 RRP rule had only just
begun. Commenters contended that renovation firms were still in the
process of working through how to achieve
[[Page 47923]]
compliance with the rule on a daily basis and that EPA should wait to
add new requirements until firms were generally comfortable with the
requirements promulgated in 2008. Commenters also argued that EPA
should not make a determination that additional requirements are needed
without first carefully assessing the status and impact of the existing
RRP rule when fully implemented. EPA agrees with the general principle
expressed by these commenters--that it is premature to impose
significant additional work practice requirements for renovations
already covered by the RRP rule, particularly given the information
before the Agency. EPA also agrees that many renovation firms are still
determining what the RRP rule requires from them on renovation
projects. EPA also acknowledges that there are practical implementation
issues with promulgating a significant change so soon after thousands
of renovators have become certified renovators, and have taken the
required training, which did not include information on the proposed
dust wipe testing or clearance requirements.
Some commenters suggested that EPA concentrate on RRP education and
outreach at this time, rather than on additional requirements. EPA
agrees that outreach and education on lead poisoning in general, and
the link between renovations and increased blood lead levels in
particular, continues to be important. As part of the RRP program's
Lead-Safe Certified media campaign, EPA developed and made available to
the public outreach materials aimed at both contractors and consumers.
The materials include a Public Service Advertising (PSA) advertisement
aimed at contractors, banners for Web sites, sample articles for
magazines, newsletters or other publications to help inform contractors
about the rule, post cards and buck slips to stuff into mailers, as
well as an informational brochure about the rule for building managers.
EPA has also developed fact sheets about the RRP rule that hardware or
paint supply stores can hand out to their customers to inform them of
the regulatory requirements. All of this information is available to
the public on EPA's Web site at https://epa.gov/lead/pubs/lscp-press-materials.htm.
The Agency has also developed outreach materials for consumers in
order to build demand for lead-safe certified firms among the public.
The consumer outreach materials include consumer print advertisements,
PSA radio advertisements in English and Spanish, and a fact sheet about
the RRP rule that contractors can provide to consumers to inform them
about the advantages of hiring lead-safe renovation firms. The consumer
outreach materials are also downloadable from EPA's Web site at https://epa.gov/lead/pubs/lscp-consumers.htm.
Finally, in an effort to raise awareness of the consequences of
lead poisoning among parents and pregnant women who live in homes built
before 1978, the Coalition to End Childhood Lead Poisoning, EPA and HUD
joined the Ad Council in April 2010 to launch a national multimedia PSA
campaign. As stated in the PSA campaign press release, the most common
pathways for lead poisoning are deteriorating lead-based paint (on
older windows, doors and trim, or walls) or improperly-performed
renovation, repair and painting activities that cause paint to chip,
peel, or flake.
EPA will continue to evaluate and consider additional outreach and
educational opportunities to improve property owner and occupant
understanding of dust-lead hazards created by renovations. EPA also
will continue to monitor implementation of the RRP rule. If future
information, studies, or data indicate that the existing RRP rule work
practices are not reliable, safe, and effective, EPA will consider
whether additional requirements should be proposed.
2. Elimination of provision allowing clearance in lieu of cleaning
verification. In the 2010 proposal, EPA proposed to eliminate the
existing provision that allows renovation firms to skip the cleaning
verification part of the mandatory cleaning protocol if another
Federal, State, or local law or regulation, or the contract between the
renovation firm and the property owner requires the renovation firm to
use qualified entities to perform dust wipe testing and requires the
renovation firm to achieve clearance. The rationale for eliminating
this provision was based on the fact that, as discussed in the preamble
to the 2010 proposal and the preamble to the 2008 RRP final rule,
cleaning verification is an integral part of the whole suite of RRP
work practices. The Dust Study demonstrates that these practices, when
observed as a whole, are effective at minimizing exposure to dust-lead
hazards generated by renovations.
EPA received only a handful of comments on this aspect of the 2010
proposal. Commenters thought that removing this provision from the RRP
rule would make the rule inconsistent with the HUD regulations or State
or local laws. Some believed that requiring both cleaning verification
and clearance was unnecessarily burdensome, and pointed out that
persons trained in lead-safe work practices had been achieving
clearance without cleaning verification for a number of years now.
While EPA does not agree with all of these assertions, EPA does agree
that it is unnecessary to require renovation firms who must achieve
clearance to follow the specific cleaning verification protocol. After
all, these firms must continue to clean until they achieve the
clearance standards. As discussed in the preamble to the 2010 Proposal,
and mentioned by some commenters specifically in reference to this
provision, contractors who receive the regular feedback provided by a
clearance requirement have learned how to clean so that they typically
achieve clearance on the first attempt. Specifically, in its Evaluation
of the HUD Lead-Based Paint Hazard Control Grant Program (Ref. 10), HUD
noted that the rate of passing initial clearance was associated with
repetition of lead hazard control activities. Therefore, EPA is
retaining the provision that allows the cleaning verification step to
be skipped if the renovation firm must also achieve clearance. However,
EPA believes that renovation firms whose projects are subject to
clearance only as a result of contractual requirements are less likely
to gain the repetitive experience of cleaning sufficiently so as to
meet clearance with few cleaning cycles, so EPA encourages property
owners who include clearance in their renovation contracts to also
require renovation firms to perform cleaning verification. EPA also
notes that States and Tribes are free to include both clearance and
cleaning verification in their laws and regulations.
3. Paint chip sample collection. In May 2010, EPA proposed to give
certified renovators another option for determining whether lead-based
paint is present on components to be affected by a renovation. This
option would allow certified renovators to collect paint chip samples
from components to be affected by a renovation instead of using test
kits to test the paint on the components. The samples would be required
to be sent to an entity recognized under the NLLAP for analysis. In
issuing this 2010 proposal, EPA reasoned that it would be easy to teach
certified renovators to collect paint chip samples in the renovator
course and this would provide maximum flexibility for certified
renovators and renovation firms.
EPA received a number of comments on this part of its 2010
proposal. Some commenters supported this option
[[Page 47924]]
because they felt that it is easy to properly collect a paint chip
sample, and they agreed that this would provide additional needed
flexibility for certified renovators and renovation firms. One
commenter stated that, as a homeowner, he had been instructed by an
NLLAP laboratory over the telephone on how to properly collect a paint
chip sample and forward it to the laboratory for analysis. This
experience led him to believe that it would be feasible to include in
the renovator course instruction on how to collect a paint chip sample
and forward it for analysis. Other commenters did not support this
aspect of the 2010 proposal because they believe that only certified
inspectors or risk assessors should be permitted to collect paint chip
samples or make determinations about the presence or absence of lead-
based paint. Several noted that this would conflict with State laws
that prohibit anyone other than a certified inspector or risk assessor
from sampling for lead-based paint. Some commenters expressed concern
about the length of the renovator course, and the ability to add the
additional information on paint chip collection, including information
on chain-of-custody issues and laboratory submission procedures,
without lengthening the course beyond 8 hours. Others noted that
renovators are already being taught many of the necessary skills during
instruction on how to properly use test kits.
Because renovator training courses are already required to include
training in how and where to use test kits, and the associated
recordkeeping requirements, EPA agrees with those commenters who
believed that it would take very little additional time to also provide
renovators with specific training in how to collect a chip sample and
submit it for analysis. The selection of locations to test and the
recordkeeping requirements would be identical whether test kits or
paint chip sampling is used, except that the laboratory report would
also have to be maintained along with the records associated with the
renovation. EPA also agrees with those commenters who thought that this
option would provide additional important flexibility. EPA is
promulgating the proposed option allowing certified renovators to
collect paint chip samples from painted components that will be
disturbed by a renovation and submit those samples to an NLLAP-
recognized entity for analysis. EPA will modify the model certified
renovator training course to add the necessary information on sample
collection, chain-of-custody, and laboratory submission procedures. One
commenter wondered how renovators who have already taken the training
to become certified would learn about this option and how to use it.
EPA will post the information developed for the renovator training
course on its Web site. EPA will also e-mail this information to
certified renovation firms that provided an e-mail address on their
certification applications. As pointed out by several commenters, paint
chip sample collection, by itself, is a relatively simple thing to
learn and EPA believes that certified renovators who have already been
trained in how to properly use a test kit will be able to learn how to
properly collect a paint chip sample and submit it to an NLLAP-
recognized entity from the material EPA posts on its Web site.
At least one commenter pointed out that EPA would also have to
modify the recordkeeping requirements to accommodate this option and
include information specific to paint chip sample collection, such as
component and location tested, identity of the NLLAP entity analyzing
the samples, and the sample results. Accordingly, EPA is modifying 40
CFR 745.86(b)(1) to add a new subparagraph (iii) that requires records
pertaining to paint chip sample collection and analysis, including a
description of the components that were sampled, and the locations
sampled, the name and address of the NLLAP-recognized entity performing
the analysis, and the results for each sample. EPA is also modifying 40
CFR 745.86(b)(6) to include a certification by the certified renovator
that, if paint chip samples were collected, that the samples were
collected from the components in the locations specified, that the
samples were submitted for analysis to the identified NLLAP-recognized
entity, and that the sample results were as specified.
This option does not make certified renovator the equivalent of a
certified lead-based paint inspector. Certified renovators must still
test each affected component, they are not permitted to exclude
components based on similar painting histories or perform random paint
sampling in multi-unit buildings. Just as with the current provisions
for test kit use, in those states that do not permit persons other than
certified inspectors or risk assessors to sample or test for lead-based
paint, certified renovators will not be able to exercise this option.
4. Training provider accreditation. In May 2010, EPA proposed a
number of minor changes to the training provider accreditation
provisions. EPA received very little public comment on these proposed
amendments, and EPA is promulgating these amendments as proposed.
a. Documentation of personnel qualifications. The first of these
minor amendments involves submission of documentation of training
program manager and principal instructor qualifications along with
training provider applications for accreditation. Training providers
who wish to provide renovator, dust sampling technician, or lead-based
paint activities training for Federal certification purposes must apply
for and receive accreditation from EPA. To become accredited, a
provider must employ a training program manager as well as principal
instructor(s) who meet certain education, training and work experience
requirements. The training provider must indicate on its application
for accreditation that the training program manager and principal
instructor(s) meet these requirements; however, the 2008 RRP rule did
not require documentation (e.g., resumes) regarding the qualifications
of these individuals to be submitted to EPA. The Agency believes it is
important to review this information when determining whether to
approve a training provider application. When EPA reviews applications
for accreditation, it is common for the Agency to request this
documentation from training providers in order to verify that the
training program manager and principal instructor(s) have the proper
qualifications. Requesting this information takes time and can delay
the review of an application. Therefore, the Agency will now require
training providers to submit documentation regarding the qualifications
of the education, training and work experience of training managers and
principal instructors with their applications for accreditation. Only
one commenter commented on this provision, expressing general support
for the change.
b. Submission of training course materials. EPA is also
promulgating other proposed changes to the required materials that must
be submitted along with an accreditation application. EPA received only
one comment expressing general support for this proposed change.
Specifically, to become accredited, a training provider must submit a
copy of its training course materials with its application for
accreditation for review by the Agency. If a training provider chooses
to use the model course developed by EPA or a course approved by an
authorized State or Indian Tribe, then the provider is not
[[Page 47925]]
currently required to submit the course materials with its application.
Instead, the training provider indicates on its application that it
will use the EPA model course or a course approved by an authorized
State or Indian Tribe. Authorized States and Indian Tribes can have
renovation or abatement programs that are significantly different from
the EPA-administered program which would be reflected in their approved
course materials. In these instances, a training course approved by the
State or Indian Tribe may not be sufficient for the purposes of
training someone on the requirements of the Federal program.
Accordingly, the Agency proposed to require training providers who
apply to EPA for accreditation and wish to use a course approved by an
authorized State or Indian Tribe to submit the course materials for EPA
review. EPA reasoned that this will give the Agency the opportunity to
identify and address any significant differences between the
requirements of EPA and the authorized program that may appear in the
course so the Agency can ensure that EPA-accredited training providers
are using appropriate course materials.
EPA is promulgating this provision as proposed. This provision only
applies to those training providers who wish to use a training course
approved by an authorized State or Indian Tribe that is different from
the EPA model training course. Training providers wishing to use the
EPA model courses need not submit those materials with their
applications.
c. Role of principal instructor. EPA is promulgating a proposed
minor amendment involving a clarification of the role of principal
instructors in teaching courses. The regulation, at 40 CFR
745.225(c)(3), states that principal instructors are responsible for
the organization of their courses and oversight of the teaching of all
course material. The regulations also define ``principal instructor''
as ``the individual who has the primary responsibility for organizing
and teaching a particular course.'' Nonetheless, the rule also allows
training program managers to designate experts in a particular field
(e.g., doctors or lawyers) as guest instructors, on an as needed basis,
to teach discrete portions of the course. EPA interprets these
provisions to require a principal instructor to be present and
primarily responsible for teaching the course, although guest
instructors may be used to teach some portion(s) of the course.
Principal instructors are also responsible for the quality of the
instruction delivered by the guest instructors. To ensure that the
regulation is clear on this point, EPA proposed to amend 40 CFR
745.225(c)(3) to state that principal instructor(s) are primarily
responsible for teaching the course materials and must be present to
provide instruction (or oversight of portions of the course taught by
guest instructors) for the course for which he has been designated the
principal instructor. EPA received two comments on this provision, both
supported the change, and one specifically stated a belief that having
principal instructors present while guest lecturers teach would improve
the content of many courses. EPA agrees with these commenters and EPA
is promulgating this provision as proposed.
d. Application amendments. EPA is promulgating as proposed another
minor amendment involving a specific provision requiring training
providers to amend their accreditation application whenever there is a
change to the information presented in their most recent accreditation
or re-accreditation application. The RRP rule includes requirements for
amending the certification of a renovation firm. Firms must submit an
amendment within 90 days of the date that a change occurs to
information in its most recent application for certification or re-
certification. Examples of amendments include a change in the firm's
name without transfer of ownership, or a change of address or other
contact information. To amend its certification, a firm must submit an
application, noting on the form that it was submitted as an amendment.
The firm must complete the sections of the application pertaining to
the new information, and sign and date the form. EPA has interpreted
the training provider accreditation regulations to require accredited
training providers to submit amended applications whenever there is a
change to the information provided in the training provider's most
recent application for accreditation or re-accreditation, including
information regarding the training manager and any principal
instructor(s) teaching courses offered by the training provider.
However, the existing regulations do not specify a time limit for
submitting an amendment, so EPA proposed to require training providers
to submit amendments within 90 days of the date a change occurs to
information in each provider's most recent application. As proposed, if
the training provider does not amend its most recent accreditation
application within the 90-day time period, it must stop providing
training until the accreditation application is amended. EPA also
proposed to approve or disapprove amendments for a new training
manager, any new or additional principal instructors, or any new
permanent training location within 30 days of the date EPA receives the
amendment. This 30-day time period will give EPA time to check the
qualifications of the training manager(s) or principal instructor(s)
before the training manager begins managing or the principal instructor
begins teaching a course. This 30-day time period also gives EPA time
to verify the suitability of a new permanent training location by
visiting the location. As proposed, the training provider would not be
permitted to provide training under the new training manager or offer
courses taught by any new principal instructor(s) or at the new
training location until EPA either approves the amendment or 30 days
has passed. EPA also proposed to clarify that no fee will be charged
for accreditation application or certification amendments. EPA received
no comments on this proposed amendment.
Because qualified training managers and principal instructors are
critical to ensuring effective training, it is important for EPA to
have the ability to review their qualifications before they begin to
provide training. If unqualified individuals provide training, it could
be very difficult to determine whether the trainees received adequate
training and resolve any concerns over the quality of the training.
Requiring retraining would not only inconvenience the training
provider, it would also be burdensome for the trainees themselves.
Therefore, EPA is promulgating the 30-day review period for new
training managers and principal instructors as proposed, with several
modifications. The first relates to the calculation of the 30-day
review period. EPA is clarifying that the 30-day period begins upon
submission of a complete application for amendment. Thus, if the
amendment involves a new training manager or principal instructor, the
training provider must fill out the section of the application that
identifies the training provider and the sections that pertain to the
new training manager or principal instructor, sign the application, and
include the individual's qualifications along with the application for
amendment. If the application does not include these items, then the
30-day review period would not begin until the missing information is
submitted.
In addition, in further reviewing this proposed provision, EPA has
decided that additional flexibility would be beneficial for training
providers. If the training provider wishes to use a
[[Page 47926]]
training manager or principal instructor who has already been reviewed
by EPA as part of a successful application for training provider
accreditation under 40 CFR 745.225, whether for that training provider
or another, the training provider may do so on an interim basis without
delay. The training manager or principal instructor must still meet the
qualifications for the position as described in 40 CFR 745.225(c)(1)-
(2). If, within 30 days of the date that the training provider begins
using such an individual as a new training manager or principal
instructor, EPA determines that the individual should not be used in
such a capacity, EPA will provide written notice to the training
provider. The training provider must stop providing training under the
new training manager or principal instructor upon receipt of written
notice from EPA.
With respect to new permanent training locations, EPA is also
concerned that a poor choice of location could negatively affect the
quality of training. For example, if a location is chosen that does not
have a suitable surface for performing cleaning verification, trainees
would be unable to experience actually doing, during the hands-on
portion of the course, something that will be an important part of
their responsibilities as certified renovators. However, EPA believes
that the choice of training location does not, in most cases, have as
big of an impact on the quality of training as the training manager or
the principal instructor. During the accreditation process for new
training providers, it has been EPA's practice to review the
qualifications for each and every training manager and principal
instructor named on an application. In contrast, where a training
provider has identified multiple permanent training locations in its
application, EPA has chosen to visit a sample of locations, rather than
each and every location. In addition, EPA has been approving traveling
training providers based on the criteria that the providers will use to
select a training location, a demonstration of the hands-on training,
and an examination of the equipment the providers plan to use in
training. Therefore, EPA will allow training providers to use new
permanent training locations on an interim basis for 30 days. If,
during that 30 days, EPA determines that the location is not adequate,
the training provider must stop using that location upon written notice
from EPA.
e. Hands-on training requirements. Another minor amendment involves
the topics for which hands-on training is required in the renovator and
dust sampling technician courses. The regulations at 40 CFR 745.225
includes requirements and procedures that training programs must follow
to become accredited in order to provide instruction in lead-based
paint courses. Minimum requirements for training curricula are found in
this section, which lists course topics that must be included in the
different training courses with an indication of the topics that
require hands-on instruction. However, EPA inadvertently omitted
indicating which course topics required hands-on training for the
renovator and dust sampling technician disciplines. Accordingly, EPA
proposed to identify in 40 CFR 745.225(d) which topics in the renovator
and dust sampling technician courses require hands-on training. In
further clarification, EPA also proposed to add a sentence to 40 CFR
745.225(e)(2) stating