Findings of Failure To Attain the 1997 PM2.5, 69448-69454 [2016-24084]
Download as PDF
69448
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
ECCS rulemaking and stated that PRM–
50–75 would be addressed by
alternative means. The NRC will issue a
separate Federal Register document to
disposition PRM–50–75.
The NRC is no longer pursuing the
‘‘Risk-Informed Changes to Loss-OfCoolant Accident Technical
Requirements’’ rulemaking for the
reasons discussed in this document. In
the next edition of the Unified Agenda,
the NRC will update the entry for this
rulemaking and reference this document
to indicate that the 50.46a ECCS
rulemaking is no longer being pursued.
This rulemaking activity will appear in
the completed section of that edition of
the Unified Agenda, but will not appear
in subsequent editions. If the NRC
decides to pursue a similar or related
rulemaking in the future, it will inform
the public through a new rulemaking
entry in the Unified Agenda.
Dated at Rockville, Maryland, this 13th day
of September 2016.
For the Nuclear Regulatory Commission.
Victor M. McCree,
Executive Director for Operations.
[FR Doc. 2016–24189 Filed 10–5–16; 8:45 am]
BILLING CODE 7590–01–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[EPA–R09–OAR–2016–0494; FRL–9953–65–
Region 9]
Findings of Failure To Attain the 1997
PM2.5 Standards; California; San
Joaquin Valley
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
The Environmental Protection
Agency (EPA) is proposing to determine
that the San Joaquin Valley
nonattainment area failed to attain the
1997 annual and 24-hour fine
particulate matter (PM2.5) national
ambient air quality standards by the
December 31, 2015 ‘‘Serious’’ area
attainment date. This proposed
determination is based upon monitored
air quality data from 2013 through 2015.
If the EPA finalizes this determination
as proposed, the State of California will
be required to submit a revision to the
California State Implementation Plan
that, among other elements, provides for
expeditious attainment of the 1997
PM2.5 standards and for a five percent
annual reduction in the emissions of
sradovich on DSK3GMQ082PROD with PROPOSALS
SUMMARY:
18:26 Oct 05, 2016
Any comments must arrive by
November 7, 2016.
DATES:
Submit your comments,
identified by Docket ID No. EPA–R09–
OAR–2016–0494 at https://
www.regulations.gov, or via email to
Rory Mays at mays.rory@epa.gov. For
comments submitted at Regulations.gov,
follow the online instructions for
submitting comments. Once submitted,
comments cannot be edited or removed
from Regulations.gov. For either manner
of submission, the EPA may publish any
comment received to its public docket.
Do not submit electronically any
information you consider to be
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute. Multimedia
submissions (audio, video, etc.) must be
accompanied by a written comment.
The written comment is considered the
official comment and should include
discussion of all points you wish to
make. The EPA will generally not
consider comments or comment
contents located outside of the primary
submission (i.e., on the Web, cloud, or
other file sharing system). For
additional submission methods, please
contact the person identified in the FOR
FURTHER INFORMATION CONTACT section.
For the full EPA public comment policy,
information about CBI or multimedia
submissions, and general guidance on
making effective comments, please visit
https://www2.epa.gov/dockets/
commenting-epa-dockets.
ADDRESSES:
V. Conclusion
VerDate Sep<11>2014
direct PM2.5 or a PM2.5 plan precursor
pollutant.
Jkt 241001
Rory
Mays, Air Planning Office (AIR–2), EPA
Region 9, (415) 972–3227, mays.rory@
epa.gov.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we’’, ‘‘us’’
and ‘‘our’’ refer to the EPA.
Table of Contents
I. Background
A. PM2.5 NAAQS
B. San Joaquin Valley Designations,
Classifications, and Attainment Dates for
1997 PM2.5 NAAQS
II. Proposed Determination and
Consequences
A. Applicable Statutory and Regulatory
Provisions
B. Monitoring Network Considerations
C. Data Considerations and Proposed
Determination
D. Consequences for Serious PM2.5
Nonattainment Area Failing To Attain
Standards by Attainment Date
III. Proposed Action and Request for Public
Comment
IV. Statutory and Executive Order Reviews
PO 00000
Frm 00003
Fmt 4702
Sfmt 4702
I. Background
A. PM2.5 NAAQS
Under section 109 of the Clean Air
Act (CAA or ‘‘Act’’), the EPA has
established national ambient air quality
standards (NAAQS or ‘‘standards’’) for
certain pervasive air pollutants (referred
to as ‘‘criteria pollutants’’) and conducts
periodic reviews of the NAAQS to
determine whether they should be
revised or whether new NAAQS should
be established.
On July 1, 1987 (52 FR 24634), the
EPA replaced the original standard for
particulate matter, measured as total
suspended particulate matter (TSP) (i.e.,
particles roughly 30 micrometers or
less), with new standards that replaced
TSP as the indicator for particulate
matter with a new indicator that
includes only those particles with an
aerodynamic diameter less than or equal
to a nominal 10 micrometers (PM10).
On July 18, 1997 (62 FR 38652), the
EPA revised the standards for
particulate matter by establishing new
standards for particles with an
aerodynamic diameter less than or equal
to a nominal 2.5 micrometers (PM2.5).
The EPA established primary and
secondary annual and 24-hour
standards for PM2.5.1 The annual
primary and secondary standards were
set at 15.0 micrograms per cubic meter
(mg/m3), based on a 3-year average of
annual mean PM2.5 concentrations, and
the 24-hour primary and secondary
standards were set at 65 mg/m3, based on
the 3-year average of the 98th percentile
of 24-hour PM2.5 concentrations at each
monitoring site within an area. See 40
CFR 50.7. Collectively, we refer herein
to the 1997 24-hour and annual PM2.5
NAAQS as the ‘‘1997 PM2.5 NAAQS’’ or
‘‘1997 PM2.5 standards.’’ 2 The EPA
1 For a given air pollutant, ‘‘primary’’ NAAQS are
those determined by the EPA as requisite to protect
the public health, allowing an adequate margin of
safety, and ‘‘secondary’’ standards are those
determined by the EPA as requisite to protect the
public welfare from any known or anticipated
adverse effects associated with the presence of such
air pollutant in the ambient air. See CAA section
109(b).
2 On October 17, 2006 (71 FR 61144), the EPA
revised the level of the 24-hour PM2.5 standards to
35 mg/m3, and on January 15, 2013 (78 FR 3086),
the EPA revised the primary annual PM2.5 standard
to a level of 12.0 mg/m3. We recently published a
final rule revoking the 1997 primary annual PM2.5
NAAQS for areas designated (or redesignated)
attainment for that standard and revising the
regulations governing implementation of the PM2.5
standards. See 81 FR 58010 (August 24, 2016).
However, because the San Joaquin Valley remains
designated nonattainment for the 1997 annual
primary PM2.5 standard, the 1997 primary annual
PM2.5 standard will remain in effect in the San
Joaquin Valley under the EPA’s recent PM2.5
implementation rule until such time as the area is
redesignated to attainment for that standard. Thus,
even though the EPA has lowered the 24-hour and
E:\FR\FM\06OCP1.SGM
06OCP1
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
established these standards after
considering substantial evidence from
numerous health studies demonstrating
that serious health effects are associated
with exposures to PM2.5 concentrations
above these levels.
Epidemiological studies have shown
statistically significant correlations
between elevated PM2.5 levels and
premature mortality. Other important
health effects associated with PM2.5
exposure include aggravation of
respiratory and cardiovascular disease
(as indicated by increased hospital
admissions, emergency room visits,
absences from school or work, and
restricted activity days), changes in lung
function and increased respiratory
symptoms. There is also new evidence
for more subtle indicators of
cardiovascular health. Individuals
particularly sensitive to PM2.5 exposure
include older adults, people with heart
and lung disease, and children.3
PM2.5 can be emitted directly into the
atmosphere as a solid or liquid particle
(primary PM2.5 or direct PM2.5) or can be
formed in the atmosphere as a result of
various chemical reactions from
precursor emissions of nitrogen oxides,
sulfur oxides, volatile organic
compounds, and ammonia (secondary
PM2.5).4
sradovich on DSK3GMQ082PROD with PROPOSALS
B. San Joaquin Valley Designations,
Classifications, and Attainment Dates
for 1997 PM2.5 NAAQS
Following promulgation of a new or
revised NAAQS, the EPA is required
under CAA section 107(d) to designate
areas throughout the nation as attaining
or not attaining the NAAQS. On January
5, 2005, the EPA published initial air
quality designations for the 1997 annual
and 24-hour PM2.5 NAAQS, using air
quality monitoring data for the threeyear periods of 2001–2003 and 2002–
2004.5 These designations became
effective April 5, 2005.6 The EPA
designated the San Joaquin Valley area
as nonattainment for both the 1997
annual PM2.5 standards and the 1997 24hour PM2.5 standards.7
The San Joaquin Valley PM2.5
nonattainment area encompasses over
annual PM2.5 standards, the original 1997 PM2.5
standards remain in effect in the San Joaquin Valley
and represent the standards for which today’s
proposed determination are made.
3 EPA, Air Quality Criteria for Particulate Matter,
No. EPA/600/P–99/002aF and EPA/600/P–99/
002bF, October 2004.
4 80 FR 15340, 15342 (March 23, 2015).
5 70 FR 944 (January 5, 2005).
6 Id.
7 40 CFR 81.305. The 2001–2003 design values for
the San Joaquin Valley were 21.8 mg/m3 for the
annual standard and 82 mg/m3 for the 24-hour
standard. See EPA design value workbook dated
August 28, 2014, worksheets ‘‘Table 3a’’ and ‘‘Table
3b.’’
VerDate Sep<11>2014
18:26 Oct 05, 2016
Jkt 241001
69449
23,000 square miles and includes all or
part of eight counties: San Joaquin,
Stanislaus, Merced, Madera, Fresno,
Tulare, Kings, and the valley portion of
Kern.8 The area is home to four million
people and is the nation’s leading
agricultural region. Stretching over 250
miles from north to south and averaging
80 miles wide, it is partially enclosed by
the Coast Mountain range to the west,
the Tehachapi Mountains to the south,
and the Sierra Nevada range to the east.
Under state law, the California Air
Resources Board (CARB or ‘‘State’’) is
the Governor’s designee for adoption
and submittal of the state
implementation plan (SIP) and SIP
revisions to the EPA in compliance with
CAA requirements. CARB is also
generally responsible under state law for
the regulation of mobile emission
sources. Local air pollution control
districts are responsible for regulation of
stationary emission sources. In the San
Joaquin Valley, regional air quality
plans are developed by the San Joaquin
Valley Unified Air Pollution Control
District (SJVUAPCD or ‘‘District’’) with
input from CARB and typically rely on
both mobile source control measures for
which CARB is responsible and
stationary source control measures for
which the District is responsible. Once
the District adopts a regional air quality
plan, the plan is submitted to CARB for
adoption as part of the California SIP
and submittal to the EPA.
Between 2007 and 2011, California
made six SIP submissions to address
nonattainment area planning
requirements for the 1997 PM2.5 NAAQS
in the San Joaquin Valley.9 We refer to
these submissions collectively as the
‘‘2008 PM2.5 Plan.’’ On November 9,
2011, the EPA approved all elements of
the 2008 PM2.5 Plan except for the
contingency measures, which the EPA
disapproved.10 As part of that action
and pursuant to CAA section
172(a)(2)(A), the EPA granted
California’s request for an extension of
the attainment date for the San Joaquin
Valley area to April 5, 2015.11
A 2013 court decision by the U.S.
Court of Appeals for the D.C. Circuit
(‘‘D.C. Circuit’’) in Natural Resources
Defense Council v. EPA concluded that
the EPA erred in implementing the 1997
PM2.5 standards solely pursuant to the
general implementation requirements of
subpart 1, without also considering the
requirements specific to PM10
nonattainment areas in subpart 4, part D
of title I of the CAA.12 Consistent with
the NRDC decision, on June 2, 2014, the
EPA classified all areas designated
nonattainment for the 1997 or the 2006
PM2.5 standards as ‘‘Moderate’’
nonattainment areas under subpart 4.13
Because this rulemaking did not affect
any action that the EPA had previously
taken under section 110(k) of the Act on
a SIP for a PM2.5 nonattainment area, the
April 5, 2015 attainment date that the
EPA had approved for the San Joaquin
Valley area in November 2011 remained
in effect.14
On April 7, 2015, the EPA reclassified
the San Joaquin Valley area as a
‘‘Serious’’ PM2.5 nonattainment area
under subpart 4, based on the EPA’s
determination that the area could not
practicably attain the 1997 PM2.5
standards by the April 5, 2015
attainment date.15 This reclassification
was based upon the EPA’s evaluation of
ambient air quality data from the 2003–
2014 period, including the 2012–2014
design value, which indicated that it
was not practicable for certain
monitoring sites within the San Joaquin
Valley area to show PM2.5 design values
at or below the level of the 1997 PM2.5
NAAQS by April 5, 2015.16
As a consequence of reclassification
as a Serious PM2.5 nonattainment area,
the San Joaquin Valley area became
subject to a new attainment date under
CAA section 188(c)(2) and the
requirement to submit a Serious area
plan that satisfies the requirements of
part D of title I of the Act, including the
requirements of subpart 4, for the 1997
PM2.5 NAAQS.17 Under subpart 4, the
attainment date for an area classified as
Serious is as expeditiously as
8 For a precise description of the geographic
boundaries of the San Joaquin Valley PM2.5
nonattainment area, see 40 CFR 81.305.
9 76 FR 69896 at n. 2 (November 9, 2011).
10 Id. at 69924.
11 Id. Under CAA section 172(a)(2)(A), the
attainment date for a nonattainment area is ‘‘the
date by which attainment can be achieved as
expeditiously as practicable, but no later than five
years from the date such area was designated
nonattainment,’’ except that EPA may extend the
attainment date as appropriate for a period no
greater than ten years from the date of designation
as nonattainment, considering the severity of
nonattainment and the availability and feasibility of
pollution control measures. CAA section
172(a)(2)(A).
12 Natural Resources Defense Council v. EPA, 706
F.3d 428 (D.C. Cir. 2013) (‘‘NRDC’’).
13 79 FR 31566 (June 2, 2014). As part of this
rulemaking, EPA established a December 31, 2014
deadline for states to submit attainment-related and
nonattainment new source review SIP elements
required for PM2.5 nonattainment areas pursuant to
subpart 4. Id.
14 Id. at 31569.
15 80 FR 18528 (April 7, 2015).
16 Id. at 18529; see also proposed rule, 80 FR 1482
(January 12, 2015). Air quality data for 2012–2014
indicated that the highest monitors in the San
Joaquin Valley area had design values of 19.7 mg/
m3 for the annual standard and 71 mg/m3 for the 24hour standard.
17 80 FR 18258 at 18530–18532.
PO 00000
Frm 00004
Fmt 4702
Sfmt 4702
E:\FR\FM\06OCP1.SGM
06OCP1
sradovich on DSK3GMQ082PROD with PROPOSALS
69450
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
practicable, but no later than the end of
the tenth calendar year following
designation. As explained in the EPA’s
final reclassification action, the Serious
area plan for the San Joaquin Valley
must include provisions to assure that
the best available control measures for
the control of direct PM2.5 and PM2.5
precursors shall be implemented no
later than 4 years after the area is
reclassified (CAA section 189(b)(1)(B)),
and a demonstration (including air
quality modeling) that the plan provides
for attainment as expeditiously as
practicable but no later than December
31, 2015, which is the latest permissible
attainment date under CAA section
188(c)(2).18
Given the December 31, 2015
outermost attainment deadline for the
San Joaquin Valley area under section
188(c)(2), the EPA noted its expectation
that the State would adopt and submit
a Serious area plan for the San Joaquin
Valley well before the statutory SIP
submission deadlines in CAA section
189(b)(2).19 The EPA also noted that, in
light of the available ambient air quality
data and the short amount of time
available before the December 31, 2015
attainment date, California could choose
to submit a request for an extension of
the Serious area attainment date
pursuant to CAA section 188(e)
simultaneously with its submission of a
Serious area plan for the area.20
California submitted its 1997 PM2.5
Serious area plan for the San Joaquin
Valley in two submittals dated June 25,
2015 and August 13, 2015, including a
request under section 188(e) to extend
the attainment date for the 1997 24-hour
PM2.5 NAAQS by three years (to
December 31, 2018) and to extend the
attainment date for the 1997 annual
PM2.5 NAAQS by five years (to
December 31, 2020). The EPA proposed
to approve most of the San Joaquin
Valley 1997 PM2.5 Serious area plan, to
conditionally approve the Plan’s
quantitative milestones, to disapprove
the plan’s contingency measures, and to
grant the requested attainment date
extensions.21 We received adverse
comments on our proposal on several
aspects of the plan and its control
measures. Upon further evaluation of
the plan and after consideration of the
comments, the EPA decided it could no
longer support an action to extend the
attainment date for the San Joaquin
18 Id.
19 Id.
at 18531.
20 Id.
21 81
FR 6936 (February 9, 2016).
VerDate Sep<11>2014
18:26 Oct 05, 2016
Jkt 241001
Valley Serious PM2.5 nonattainment area
for the 1997 PM2.5 NAAQS.22
Since the EPA has not approved the
requested attainment date extensions,
the applicable attainment date remains
December 31, 2015 for the San Joaquin
Valley with respect to the 1997 PM2.5
NAAQS. As discussed in section II of
this proposed rule, the EPA must
determine, based on air quality data as
of the attainment date, whether an area
attained the applicable NAAQS by its
attainment date.
II. Proposed Determination and
Consequences
A. Applicable Statutory and Regulatory
Provisions
Sections 179(c)(1) and 188(b)(2) of the
CAA require the EPA to determine
whether a PM2.5 nonattainment area
attained the applicable PM2.5 standards
by the applicable attainment date, based
on the area’s air quality as of the
attainment date.
A determination of whether an area’s
air quality meets the PM2.5 standards is
generally based upon the most recent
three years of complete, quality-assured
data gathered at established State and
Local Air Monitoring Stations (SLAMS)
in a nonattainment area and entered
into the EPA’s Air Quality System
(AQS) database. Data from ambient air
monitors operated by state/local
agencies in compliance with the EPA
monitoring requirements must be
submitted to AQS. Monitoring agencies
annually certify that these data are
accurate to the best of their knowledge.
Accordingly, the EPA relies primarily
on data in AQS when determining the
attainment status of areas. See 40 CFR
50.7; 40 CFR part 50, Appendix L; 40
CFR part 53; 40 CFR part 58, and 40
CFR part 58, Appendices A, C, D, and
E. All data are reviewed to determine
the area’s air quality status in
accordance with 40 CFR part 50,
Appendix N.
Under EPA regulations in 40 CFR part
50, § 50.7 and in accordance with
Appendix N, the 1997 annual PM2.5
standards are met when the design
value is less than or equal to 15.0 mg/
m3 (based on the rounding convention
in 40 CFR part 50, Appendix N) at each
eligible monitoring site within the
area.23 Data completeness requirements
22 See U.S. EPA, Final rule, ‘‘Denial of Request for
Extension of Attainment Date for 1997 PM2.5
NAAQS; California; San Joaquin Valley Serious
Nonattainment Area,’’ to be published in the same
edition of the Federal Register as this proposed
rule, and U.S. EPA Fact Sheet, ‘‘San Joaquin Valley
Fine Particulate Matter,’’ June 29, 2016.
23 The annual PM
2.5 standard design value is the
3-year average of annual mean concentration, and
the 1997 annual PM2.5 NAAQS are met when the
PO 00000
Frm 00005
Fmt 4702
Sfmt 4702
for a given year are met when at least
75 percent of the scheduled sampling
days for each quarter have valid data.
Under EPA regulations in 40 CFR part
50, section 50.7 and in accordance with
Appendix N, the 1997 24-hour PM2.5
standards are met when the design
value is less than or equal to 65 mg/m3
(based on the rounding convention in 40
CFR part 50, Appendix N) at each
eligible monitoring site within the
area.24 Data completeness requirements
for a given year are met when at least
75 percent of the scheduled sampling
days for each quarter have valid data.
B. Monitoring Network Considerations
Section 110(a)(2)(B)(i) of the CAA
requires states to establish and operate
air monitoring networks to compile data
on ambient air quality for all criteria
pollutants. Our monitoring
requirements are specified by regulation
in 40 CFR part 58. These requirements
are applicable to state, and where
delegated, local air monitoring agencies
that operate criteria pollutant monitors.
Our regulations in 40 CFR part 58
establish specific requirements for
operating air quality surveillance
networks to measure ambient
concentrations of PM2.5, including
requirements for measurement methods,
network design, quality assurance
procedures, and in the case of large
urban areas, the minimum number of
monitoring sites designated as SLAMS.
In section 4.7 of Appendix D to 40
CFR part 58, the EPA specifies
minimum monitoring requirements for
PM2.5 to operate at SLAMS. SLAMS
produce data that are eligible for
comparison with the NAAQS, and
therefore, the monitor must be an
approved federal reference method
(FRM), federal equivalent method
(FEM), or approved regional method
(ARM). The minimum number of
SLAMS required is described in section
4.7.1, and can be met by either filterbased or continuous FRMs or FEMs. The
monitoring regulations also provide that
each core-based statistical area must
operate a minimum number of PM2.5
continuous monitors (section 4.7.2);
however, this requirement can be met
by either an FEM or a non-FEM
continuous monitor, and the continuous
monitors can be located with other
SLAMS or at a different location.
annual standard design value at each eligible
monitoring site is less than or equal to 15.0 mg/m3.
24 The 24-hour PM
2.5 standard design value is the
3-year average of annual 98th percentile 24-hour
average values recorded at each eligible monitoring
site, and the 1997 24-hour PM2.5 NAAQS are met
when the 24-hour standard design value at each
such monitoring site is less than or equal to 65 mg/
m 3.
E:\FR\FM\06OCP1.SGM
06OCP1
sradovich on DSK3GMQ082PROD with PROPOSALS
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
Consequently, the monitoring
requirements for PM2.5 can be met with
filter-based FRMs/FEMs, continuous
FEMs, continuous non-FEMs, or a
combination of monitors at each
required SLAMS.
Under 40 CFR 58.10, states are
required to submit Annual Network
Plans for ambient air monitoring
networks for approval by the EPA.
Within the San Joaquin Valley, CARB
and the District are the agencies
responsible for assuring that the area
meets air quality monitoring
requirements. The District submits
annual monitoring network plans to the
EPA that describe the various
monitoring sites operated by the District
as well as those operated by CARB
within the San Joaquin Valley. These
plans discuss the status of the air
monitoring network, as required under
40 CFR 58.10. The most recent plan
submitted by the District is the 2015 Air
Monitoring Network Plan, dated August
28, 2015. The EPA regularly reviews
these Annual Network Plans for
compliance with the applicable
reporting requirements in 40 CFR part
58. On December 28, 2015, the EPA
approved those portions of the 2015 Air
Monitoring Network Plan that pertain to
the adequacy of the network for PM2.5
monitoring purposes.25
During the 2013–2015 period, PM2.5
ambient concentration data that is
eligible for use in determining whether
an area has attained the PM2.5 NAAQS
were collected at a total of 17 sites
within the San Joaquin Valley: four sites
in Fresno County; three sites in Kern
County; two sites each in Kings,
Merced, San Joaquin, and Stanislaus
counties; and one site each in Madera
and Tulare counties. The District
operates 10 of these sites while CARB
operates seven of the sites. Fourteen of
the sites are designated SLAMS for
PM2.5. Three of the sites are designated
as special purpose monitors (i.e., the
Merced (Coffee Street), Tranquility, and
Hanford sites), but the PM2.5 data
collected there are eligible for use in
determining PM2.5 NAAQS compliance
due to the duration of monitoring at the
site and the use of FRM or FEM
monitors consistent with EPA quality
assurance requirements and siting
criteria.26 The primary monitors are
25 Letter dated December 28, 2015, from Meredith
Kurpius, Manager, EPA Region 9, Air Quality
Analysis Office, to Sheraz Gill, Director of
Strategies and Incentives, SJVUAPCD.
26 There are a number of other PM
2.5 monitoring
sites within the valley, including other sites
VerDate Sep<11>2014
18:26 Oct 05, 2016
Jkt 241001
FRMs at 11 of the 17 sites and beta
attenuation monitor FEMs at six of the
17 sites.
Based on our review of the PM2.5
monitoring network as summarized
above, we find that monitoring network
in the San Joaquin Valley is adequate for
the purpose of collecting ambient PM2.5
concentration data for use in
determining whether the San Joaquin
Valley attained the 1997 PM2.5 NAAQS
by the December 31, 2015 attainment
date.
C. Data Considerations and Proposed
Determination
Under 40 CFR 58.15, monitoring
agencies must certify, on an annual
basis, data collected at all SLAMS and
at all FRM, FEM, and ARM SPM
stations that meet EPA quality assurance
requirements. In doing so, monitoring
agencies must certify that the previous
year of ambient concentration and
quality assurance data are completely
submitted to AQS and that the ambient
concentration data are accurate to the
best of her or his knowledge. CARB
annually certifies that the data the
agency submits to AQS are quality
assured, including data collected by
CARB at monitoring sites in the San
Joaquin Valley.27 SJVUAPCD does the
same for data submitted to AQS from
monitoring sites operated by the
District.28
As noted above, CAA sections
179(c)(1) and 188(b)(2) require the EPA
to determine whether a PM2.5
nonattainment area attained the
applicable PM2.5 standards by the
applicable attainment date, based on the
area’s air quality ‘‘as of the attainment
date.’’ For the San Joaquin Valley, for
reasons discussed above, the applicable
attainment date is December 31, 2015
with respect to the 1997 PM2.5 NAAQS.
Because determinations of PM2.5
NAAQS compliance, in accordance with
40 CFR part 50, Appendix N, are based
operated by the District, the National Park Service,
and certain Indian tribes, but the data collected
from these sites are non-regulatory and not eligible
for use in determining whether the San Joaquin
Valley has attained the PM2.5 NAAQS.
27 See, e.g., letter from Ravi Ramalingam, Chief,
Consumer Products and Air Quality Assessment
Branch, CARB, to Elizabeth Adams, Acting Director,
Air Division, EPA Region 9, certifying calendar year
2015 ambient air quality data and quality assurance
data, dated May 10, 2016.
28 See, e.g., letter from Jon Klassen, Program
Manager, SJVUAPCD, letter to Deborah Jordan,
Director, Air Division, EPA Region 9, certifying
calendar year 2015 ambient air quality data and
quality assurance data, dated May 9, 2016.
PO 00000
Frm 00006
Fmt 4702
Sfmt 4702
69451
on three calendar years of data, to
determine the San Joaquin Valley’s air
quality as of December 31, 2015, we
must review the data collected during
the three-year period immediately
preceding December 31, 2015, i.e.,
January 1, 2013–December 31, 2015.
Thus, we verified that the data for the
2013–2015 period have been certified by
the relevant monitoring agencies, and
then we reviewed the data for
completeness. We note above the most
recent annual data certifications from
CARB and the District. With respect to
completeness, we determined that the
data collected by CARB and the District
meet the quarterly completeness
criterion for all 12 quarters of the threeyear period at most of the PM2.5
monitoring sites in the San Joaquin
Valley.
More specifically, among the 17 PM2.5
monitoring sites from which regulatory
data are available, the data from four of
the sites did not meet the 75%
completeness criterion (for each
quarter); however, the data from all but
one site (Bakersfield—Golden State
Highway) are sufficient nonetheless to
produce a valid design value for either
the annual PM2.5 NAAQS or the 24-hour
PM2.5 NAAQS pursuant to the rules
governing design value validity in 40
CFR part 50, Appendix N, sections 4.1
and 4.2. We note that monitors with
incomplete data in one or more quarters
may still produce valid design values if
the conditions for applying one of the
EPA’s data substitution tests are met.29
Table 1 and Table 2 show the annual
and 24-hour PM2.5 design values,
respectively, at each of the 17
monitoring sites within the San Joaquin
Valley nonattainment area for the
relevant three-year period (2013–2015).
The tables show that the annual PM2.5
design values for the 2013–2015 period
are greater than 15.0 mg/m3 at eight of
the sites and that the 24-hour PM2.5
design values are greater than 65 mg/m3
at four of the sites.
29 See 40 CFR part 50, Appendix N, section 4.1(b)
for the annual PM2.5 NAAQS and section 4.2(b) for
the 24-hour PM2.5 NAAQS. Each year the EPA
produces a workbook identifying PM2.5 monitors
with valid design values taking into account the
data substitution tests set forth in 40 CFR part 50,
Appendix N, section 4 where appropriate. The
workbook design values reflect the concentration
data input to AQS, but the design values calculated
therein differ for some monitors from the design
values calculated by AQS because at this time only
the workbook design values accurately accounts for
the two data substitution tests set forth in 40 CFR
part 50, Appendix N, section 4.0.
E:\FR\FM\06OCP1.SGM
06OCP1
69452
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
TABLE 1—2013–2015 ANNUAL PM2.5 DESIGN VALUES FOR THE SAN JOAQUIN VALLEY NONATTAINMENT AREA
Annual Mean (μg/m3)
Site
(AQS ID)
General location
Fresno County:
Fresno–Pacific ..............................................................................
Fresno—Garland ..........................................................................
Clovis ............................................................................................
Tranquility a ...................................................................................
Kern County:
Bakersfield—Planz Road ..............................................................
Bakersfield—California Ave. .........................................................
Bakersfield—Golden State Highway ............................................
Kings County:
Corcoran a b ...................................................................................
Hanford .........................................................................................
Madera County:
Madera—Avenue 14 .....................................................................
Merced County:
Merced—M Street .........................................................................
Merced—Coffee ............................................................................
San Joaquin County:
Stockton ........................................................................................
Manteca ........................................................................................
Stanislaus County:
Modesto ........................................................................................
Turlock ..........................................................................................
Tulare County:
Visalia ...........................................................................................
2013
2014
2015
2013–2015
Annual design values
(μg/m3)
06–019–5025
06–019–0011
06–019–5001
06–019–2009
15.9
16.8
15.9
8.3
13.8
15.1
14.8
Inc
14.1
14.4
15.0
10.0
14.6
15.4
15.2
8.7
06–029–0016
06–029–0014
06–029–0010
22.8
20.0
Inc
21.6
18.6
Inc
17.9
16.3
16.7
20.8
18.3
Inv
06–031–0004
06–031–1004
15.6
18.2
15.4
17.5
Inc
16.6
22.2
17.4
06–039–2010
17.8
14.0
13.8
15.2
06–047–2510
06–047–0003
13.5
13.3
11.2
10.8
12.6
12.8
12.5
12.3
06–077–1002
06–077–2010
17.7
11.7
12.1
9.8
12.8
12.6
14.2
11.4
06–099–0005
06–099–0006
14.5
15.1
11.4
12.3
Inc
14.4
Inv
13.9
06–107–2002
18.9
17.9
16.1
17.6
Notes: Inc = Incomplete data. Inv = Invalid design value due to incomplete data. Design values shown in bold type do not meet the applicable
NAAQS.
Source: EPA, AQS Design Value Report, Report Request ID: 1463864, July 15, 2016, except as otherwise noted.
a Source: EPA, design value workbook dated July 29, 2016, worksheet ‘‘Table 5. PM
2.5 Site Listing, 2013–2015,’’ column S.
b The 2015 design value site (Corcoran-Patterson) is based on concentration data from January 1, 2013 to February 6, 2015. Data from February 7, 2015 to December 31, 2015 are not available due to a fire that destroyed the site. Based on design value calculation methodologies described in 40 CFR part 50, Appendix N, section 4.1(b), the annual design value for Corcoran-Patterson is considered valid despite the missing
2015 data. The second highest 2013–2015 concentration (annual PM2.5 design value of 20.8 μg/m3) at Bakersfield-Planz includes data measured for three years (January 1, 2013–December 31, 2015).
TABLE 2—2013–2015 24-HOUR PM2.5 DESIGN VALUES FOR THE SAN JOAQUIN VALLEY NONATTAINMENT AREA
98th Percentile (μg/m3)
Site
(AQS ID)
sradovich on DSK3GMQ082PROD with PROPOSALS
General location
Fresno County:
Fresno—Pacific .............................................................................
Fresno–Garland ............................................................................
Clovis ............................................................................................
Tranquility a ...................................................................................
Kern County:
Bakersfield—Planz Road ..............................................................
Bakersfield—California Ave. .........................................................
Bakersfield—Golden State Highway a ..........................................
Kings County:
Corcoran b .....................................................................................
Hanford .........................................................................................
Madera County:
Madera—Avenue 14 .....................................................................
Merced County:
Merced—M Street .........................................................................
Merced—Coffee ............................................................................
San Joaquin County:
Manteca ........................................................................................
Stockton ........................................................................................
Stanislaus County:
Modesto ........................................................................................
Turlock ..........................................................................................
Tulare County:
VerDate Sep<11>2014
19:17 Oct 05, 2016
Jkt 241001
PO 00000
Frm 00007
2013
2014
2015
2013–2015
24-Hour
design
values
(μg/m3)
06–019—5025
06–019–0011
06–019–5001
06–019–2009
71.6
63.8
56.2
35.7
61.8
66.7
64.5
Inc
42.0
52.0
45.7
35.8
58
61
55
34
06–029–0016
06–029–0014
06–029–0010
96.7
71.8
Inc
76.7
79.9
107.2
56.5
57.2
51.5
77
70
Inv
06–031–0004
06–031–1004
66.0
67.6
71.0
81.9
99.2
51.4
79
67
06–039–2010
54.6
56.0
43.7
51
06–047–2510
06–047–0003
67.3
42.3
45.9
43.8
39.0
40.3
51
42
06–077–2010
06–077–1002
40.2
56.3
40.0
44.5
42.7
39.1
41
47
06–099–0005
06–099–0006
56.4
55.4
49.5
51.2
30.8
47.3
46
51
Fmt 4702
Sfmt 4702
E:\FR\FM\06OCP1.SGM
06OCP1
69453
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
TABLE 2—2013–2015 24-HOUR PM2.5 DESIGN VALUES FOR THE SAN JOAQUIN VALLEY NONATTAINMENT AREA—
Continued
98th Percentile (μg/m3)
Site
(AQS ID)
General location
Visalia ...........................................................................................
2013
06–107–2002
2014
62.5
75.4
2015
2013–2015
24-Hour
design
values
(μg/m3)
45.8
61
sradovich on DSK3GMQ082PROD with PROPOSALS
Notes: Inc = Incomplete data. Inv = Invalid design value due to incomplete data. Design values shown in bold type do not meet the applicable
NAAQS.
Source: EPA, AQS Design Value Report, Report Request ID: 1463864, July 15, 2016, except as otherwise noted.
a Source: EPA, design value workbook dated July 29, 2016, worksheet ‘‘Table 5. PM
2.5 Site Listing, 2013–2015,’’ column Z.
b The 2015 design value site (Corcoran-Patterson) is based on concentration data from January 1, 2013 to February 6, 2015. Data from February 7, 2015 to December 31, 2015 are not available due to a fire that destroyed the site. Based on design value calculation methodologies described in 40 CFR part 50, Appendix N, section 4.2(b), the 24-hour design value for Corcoran-Patterson is considered valid despite the missing
2015 data. The second highest 2013–2015 concentration (24-hour PM2.5 design value of 77 μg/m3) at Bakersfield—Planz includes data measured for three years (January 1, 2013–December 31, 2015).
The data in Tables 1 and 2 show that
a number of sites in central and
southern San Joaquin Valley failed to
attain the 1997 annual PM2.5 NAAQS by
December 31, 2015 and that the
geographic extent of failure to attain the
1997 24-hour PM2.5 NAAQS was more
limited than for the annual standard in
that only sites in southwestern San
Joaquin Valley failed to attain the 24hour standard. The 2015 annual design
value site, i.e., the site with the highest
design value based on 2013–2015 data,
is the Corcoran site with a 2015 annual
PM2.5 design value of 22.2 mg/m3. With
respect to the 24-hour average, the 2015
design value site is the Corcoran site
with a 24-hour PM2.5 design value of 79
mg/m3.
For an area to attain the 1997 PM2.5
NAAQS by December 31, 2015, the 2015
design value (reflecting data from 2013–
2015) at each eligible monitoring site
must be equal to or less than 15.0 mg/
m3 for the annual standard and 65 mg/
m3 for the 24-hour standard. Tables 1
and 2 show that the 2015 design values
at a number of sites in the San Joaquin
Valley are greater than those values.
Therefore, based on quality-assured and
certified data for 2013–2015, we are
proposing to determine that the San
Joaquin Valley failed to attain the 1997
annual and 24-hour PM2.5 standards by
the December 31, 2015 attainment date.
Lastly, we note that, under our
regulations at 40 CFR 50.14, a
monitoring agency may request the EPA
to exclude data showing exceedances or
violations of the standard that are
directly due to an exceptional event
from use in determinations by
demonstrating that such event caused a
specific air pollution concentration at a
particular air quality monitoring
location. A monitoring agency notifies
the EPA of its intent to request
exclusion of concentrations by placing a
‘‘flag’’ in the appropriate field for the
data of concern in AQS.
VerDate Sep<11>2014
19:17 Oct 05, 2016
Jkt 241001
For PM2.5 ambient data collected from
2013–2015, the District ‘‘flagged’’ one
24-hour concentration at the Bakersfield
(Planz Road) site and two 24-hour
concentrations at the Bakersfield
(California Avenue) site due to high
winds. The District also flagged twentyfour 24-hour concentrations at each of
the Madera and Merced (Coffee Avenue)
sites due to wildfire.30
The State has not requested
concurrence on the flagged data, and
thus the data are not excluded from the
set of data used to determine whether
the standard was attained. However,
even if all of the flagged data were to be
excluded, i.e., even if the EPA had
concurred on the data as qualifying as
exceptional events, the design values
reported in Tables 1 and 2, though
slightly lower at certain sites, would
remain well above the NAAQS.31
For instance, the 2015 annual PM2.5
design value at the Bakersfield (Planz
Road) monitoring site would be 20.4 mg/
m3 instead of 20.8 mg/m3 if all of the
flagged data were excluded. Thus, it
would still fail to attain the applicable
standard of 15.0 mg/m3. Similarly, the
2015 24-hour PM2.5 design value at the
same site would be 72 mg/m3 instead of
77 mg/m3 if all of the flagged data were
excluded, thus also failing to attain the
applicable standard of 65 mg/m3.
Furthermore, several additional sites,
for which the District has not flagged
exceptional events, exceed the 1997
PM2.5 NAAQS based on 2015 annual
PM2.5 design values (i.e., FresnoGarland, Clovis, Corcoran, Hanford, and
Visalia) and 2015 24-hour design values
(i.e., Corcoran and Hanford).
30 EPA,
AQS Raw Data Qualifier Report, Report
Request ED: 1464417, July 18, 2016.
31 EPA, AQS Design Value Report, Report Request
ED: 1463865, July 15, 2016.
PO 00000
Frm 00008
Fmt 4702
Sfmt 4702
D. Consequences for Serious PM2.5
Nonattainment Area Failing To Attain
Standards by Attainment Date
The consequences for a Serious PM2.5
nonattainment area for failing to attain
the standards by the applicable
attainment date are set forth in CAA
sections 179(d) and 189(d). Under
section 179(d), a state must submit a SIP
revision for the area meeting the
requirements of CAA section 110 and
172, the latter of which requires, among
other elements, a demonstration of
attainment and reasonable further
progress, and contingency measures.
CAA section 189(d) requires that the SIP
revision must provide for attainment of
the standards and, from the date of the
SIP submittal until attainment, for an
annual reduction in the emissions of
PM2.5 or a PM2.5 plan precursor
pollutant within the area of not less
than five percent of the amount of such
emissions as reported in the most recent
inventory prepared for such area.32 The
requirement for a new attainment
demonstration under CAA section
189(d) also triggers the requirement for
the SIP revision for quantitative
milestones under section 189(c) that are
to be achieved every three years until
redesignation to attainment.
The new attainment date is set by
CAA section 179(d)(3), which relies
upon section 172(a)(2) to establish a
new attainment date but with a different
starting point than provided in section
172(a)(2). Under section 179(d)(3), the
new attainment date is the date by
which attainment can be achieved as
expeditiously as practicable, but no later
than five years from the date of the final
determination of failure to attain, except
that the EPA may extend the attainment
32 81 FR 58010 at 58100, 58158 (August 24, 2016).
The EPA defines PM2.5 plan precursor as those
PM2.5 precursors required to be regulated in the
applicable attainment plan and/or nonattainment
new source review program. 81 FR 58010 at 58152.
E:\FR\FM\06OCP1.SGM
06OCP1
69454
Federal Register / Vol. 81, No. 194 / Thursday, October 6, 2016 / Proposed Rules
date for a period no greater than 10
years from the final determination,
considering the severity of
nonattainment and the availability and
feasibility of pollution control measures.
Lastly, section 179(d) requires that the
state submit the required SIP revision
within 12 months after the applicable
attainment date. In this case, if the EPA
finalizes the proposed rule, then the
State of California will be required to
submit a SIP revision that complies with
sections 179(d) and 189(d) within 12
months of December 31, 2015, i.e., by
December 31, 2016.
sradovich on DSK3GMQ082PROD with PROPOSALS
III. Proposed Action and Request for
Public Comment
Under CAA sections 179(c)(1) and
188(b)(2), the EPA proposes to
determine that the San Joaquin Valley
‘‘Serious’’ PM2.5 nonattainment area has
failed to attain the 1997 annual and 24hour PM2.5 standards by the applicable
attainment date of December 31, 2015.
If finalized, the State of California will
be required under CAA sections 179(d)
and 189(d) to submit a revision to the
SIP for the San Joaquin Valley that,
among other elements, demonstrates
expeditious attainment of the standards
within the time period provided under
CAA section 179(d) and that provides
for annual reduction in the emissions of
PM2.5 or a PM2.5 plan precursor
pollutant within the area of not less
than five percent until attainment. The
SIP revision required under CAA
sections 179(d) and 189(d) would be
due for submittal to the EPA no later
than December 31, 2016.
The EPA is soliciting public
comments on the issues discussed in
this document. We will accept
comments from the public on this
proposal for the next 30 days. We will
consider these comments before taking
final action.
IV. Statutory and Executive Order
Reviews
This proposed action in and of itself
establishes no new requirements; it
merely documents that air quality in the
San Joaquin Valley did not meet the
1997 PM2.5 standards by the CAA
deadline. For that reason, this proposed
action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
VerDate Sep<11>2014
18:26 Oct 05, 2016
Jkt 241001
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
• Does not provide the EPA with the
discretionary authority to address
disproportionate human health or
environmental effects with practical,
appropriate, and legally permissible
methods under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this proposed action does
not have Tribal implications as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000), because
the SIP obligations discussed herein do
not apply to Indian Tribes and thus this
proposed action will not impose
substantial direct costs on Tribal
governments or preempt Tribal law.
Nonetheless, the EPA has notified the
Tribes within the San Joaquin Valley
PM2.5 nonattainment area of the
proposed action.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Ammonia,
Incorporation by reference,
Intergovernmental relations, Nitrogen
dioxide, Particulate matter, Reporting
and recordkeeping requirements, Sulfur
oxides, Volatile organic compounds.
Dated: September 23, 2016.
Alexis Strauss,
Acting Regional Administrator, Region IX.
[FR Doc. 2016–24084 Filed 10–5–16; 8:45 am]
BILLING CODE 6560–50–P
PO 00000
Frm 00009
Fmt 4702
Sfmt 4702
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–R4–ES–2016–0121;
4500030113]
RIN 1018–BB46
Endangered and Threatened Wildlife
and Plants; Threatened Species Status
for Louisiana Pinesnake
Fish and Wildlife Service,
Interior.
ACTION: Proposed rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service (Service), propose to
list the Louisiana pinesnake (Pituophis
ruthveni), a reptile species from
Louisiana and Texas, as a threatened
species under the Endangered Species
Act (Act). If we finalize this rule as
proposed, it would extend the Act’s
protections to this species.
DATES: We will accept comments
received or postmarked on or before
December 5, 2016. Comments submitted
electronically using the Federal
eRulemaking Portal (see ADDRESSES,
below) must be received by 11:59 p.m.
Eastern Time on the closing date. We
must receive requests for public
hearings, in writing, at the address
shown in FOR FURTHER INFORMATION
CONTACT by November 21, 2016.
ADDRESSES: You may submit comments
by one of the following methods:
(1) Electronically: Go to the Federal
eRulemaking Portal: https://
www.regulations.gov. In the Search box,
enter FWS–R4–ES–2016–0121, which is
the docket number for this rulemaking.
Then, click on the Search button. On the
resulting page, in the Search panel on
the left side of the screen, under the
Document Type heading, click on the
Proposed Rules link to locate this
document. You may submit a comment
by clicking on ‘‘Comment Now!’’
(2) By hard copy: Submit by U.S. mail
or hand-delivery to: Public Comments
Processing, Attn: FWS–R4–ES–2016–
0121, U.S. Fish and Wildlife Service,
MS: BPHC, 5275 Leesburg Pike, Falls
Church, VA 22041–3803.
We request that you send comments
only by the methods described above.
We will post all comments on https://
www.regulations.gov. This generally
means that we will post any personal
information you provide us (see
Information Requested, below, for more
information).
FOR FURTHER INFORMATION CONTACT: Brad
S. Rieck, Acting Field Supervisor, U.S.
Fish and Wildlife Service, Louisiana
SUMMARY:
E:\FR\FM\06OCP1.SGM
06OCP1
Agencies
[Federal Register Volume 81, Number 194 (Thursday, October 6, 2016)]
[Proposed Rules]
[Pages 69448-69454]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2016-24084]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[EPA-R09-OAR-2016-0494; FRL-9953-65-Region 9]
Findings of Failure To Attain the 1997 PM2.5 Standards;
California; San Joaquin Valley
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is proposing to
determine that the San Joaquin Valley nonattainment area failed to
attain the 1997 annual and 24-hour fine particulate matter
(PM2.5) national ambient air quality standards by the
December 31, 2015 ``Serious'' area attainment date. This proposed
determination is based upon monitored air quality data from 2013
through 2015. If the EPA finalizes this determination as proposed, the
State of California will be required to submit a revision to the
California State Implementation Plan that, among other elements,
provides for expeditious attainment of the 1997 PM2.5
standards and for a five percent annual reduction in the emissions of
direct PM2.5 or a PM2.5 plan precursor pollutant.
DATES: Any comments must arrive by November 7, 2016.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R09-
OAR-2016-0494 at https://www.regulations.gov, or via email to Rory Mays
at mays.rory@epa.gov. For comments submitted at Regulations.gov, follow
the online instructions for submitting comments. Once submitted,
comments cannot be edited or removed from Regulations.gov. For either
manner of submission, the EPA may publish any comment received to its
public docket. Do not submit electronically any information you
consider to be Confidential Business Information (CBI) or other
information whose disclosure is restricted by statute. Multimedia
submissions (audio, video, etc.) must be accompanied by a written
comment. The written comment is considered the official comment and
should include discussion of all points you wish to make. The EPA will
generally not consider comments or comment contents located outside of
the primary submission (i.e., on the Web, cloud, or other file sharing
system). For additional submission methods, please contact the person
identified in the FOR FURTHER INFORMATION CONTACT section. For the full
EPA public comment policy, information about CBI or multimedia
submissions, and general guidance on making effective comments, please
visit https://www2.epa.gov/dockets/commenting-epa-dockets.
FOR FURTHER INFORMATION CONTACT: Rory Mays, Air Planning Office (AIR-
2), EPA Region 9, (415) 972-3227, mays.rory@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, ``we'', ``us'' and
``our'' refer to the EPA.
Table of Contents
I. Background
A. PM2.5 NAAQS
B. San Joaquin Valley Designations, Classifications, and
Attainment Dates for 1997 PM2.5 NAAQS
II. Proposed Determination and Consequences
A. Applicable Statutory and Regulatory Provisions
B. Monitoring Network Considerations
C. Data Considerations and Proposed Determination
D. Consequences for Serious PM2.5 Nonattainment Area
Failing To Attain Standards by Attainment Date
III. Proposed Action and Request for Public Comment
IV. Statutory and Executive Order Reviews
I. Background
A. PM2.5 NAAQS
Under section 109 of the Clean Air Act (CAA or ``Act''), the EPA
has established national ambient air quality standards (NAAQS or
``standards'') for certain pervasive air pollutants (referred to as
``criteria pollutants'') and conducts periodic reviews of the NAAQS to
determine whether they should be revised or whether new NAAQS should be
established.
On July 1, 1987 (52 FR 24634), the EPA replaced the original
standard for particulate matter, measured as total suspended
particulate matter (TSP) (i.e., particles roughly 30 micrometers or
less), with new standards that replaced TSP as the indicator for
particulate matter with a new indicator that includes only those
particles with an aerodynamic diameter less than or equal to a nominal
10 micrometers (PM10).
On July 18, 1997 (62 FR 38652), the EPA revised the standards for
particulate matter by establishing new standards for particles with an
aerodynamic diameter less than or equal to a nominal 2.5 micrometers
(PM2.5). The EPA established primary and secondary annual
and 24-hour standards for PM2.5.\1\ The annual primary and
secondary standards were set at 15.0 micrograms per cubic meter ([mu]g/
m\3\), based on a 3-year average of annual mean PM2.5
concentrations, and the 24-hour primary and secondary standards were
set at 65 [mu]g/m\3\, based on the 3-year average of the 98th
percentile of 24-hour PM2.5 concentrations at each
monitoring site within an area. See 40 CFR 50.7. Collectively, we refer
herein to the 1997 24-hour and annual PM2.5 NAAQS as the
``1997 PM2.5 NAAQS'' or ``1997 PM2.5 standards.''
\2\ The EPA
[[Page 69449]]
established these standards after considering substantial evidence from
numerous health studies demonstrating that serious health effects are
associated with exposures to PM2.5 concentrations above
these levels.
---------------------------------------------------------------------------
\1\ For a given air pollutant, ``primary'' NAAQS are those
determined by the EPA as requisite to protect the public health,
allowing an adequate margin of safety, and ``secondary'' standards
are those determined by the EPA as requisite to protect the public
welfare from any known or anticipated adverse effects associated
with the presence of such air pollutant in the ambient air. See CAA
section 109(b).
\2\ On October 17, 2006 (71 FR 61144), the EPA revised the level
of the 24-hour PM2.5 standards to 35 [mu]g/m\3\, and on
January 15, 2013 (78 FR 3086), the EPA revised the primary annual
PM2.5 standard to a level of 12.0 [mu]g/m\3\. We recently
published a final rule revoking the 1997 primary annual
PM2.5 NAAQS for areas designated (or redesignated)
attainment for that standard and revising the regulations governing
implementation of the PM2.5 standards. See 81 FR 58010
(August 24, 2016). However, because the San Joaquin Valley remains
designated nonattainment for the 1997 annual primary
PM2.5 standard, the 1997 primary annual PM2.5
standard will remain in effect in the San Joaquin Valley under the
EPA's recent PM2.5 implementation rule until such time as
the area is redesignated to attainment for that standard. Thus, even
though the EPA has lowered the 24-hour and annual PM2.5
standards, the original 1997 PM2.5 standards remain in
effect in the San Joaquin Valley and represent the standards for
which today's proposed determination are made.
---------------------------------------------------------------------------
Epidemiological studies have shown statistically significant
correlations between elevated PM2.5 levels and premature
mortality. Other important health effects associated with
PM2.5 exposure include aggravation of respiratory and
cardiovascular disease (as indicated by increased hospital admissions,
emergency room visits, absences from school or work, and restricted
activity days), changes in lung function and increased respiratory
symptoms. There is also new evidence for more subtle indicators of
cardiovascular health. Individuals particularly sensitive to
PM2.5 exposure include older adults, people with heart and
lung disease, and children.\3\
---------------------------------------------------------------------------
\3\ EPA, Air Quality Criteria for Particulate Matter, No. EPA/
600/P-99/002aF and EPA/600/P-99/002bF, October 2004.
---------------------------------------------------------------------------
PM2.5 can be emitted directly into the atmosphere as a
solid or liquid particle (primary PM2.5 or direct
PM2.5) or can be formed in the atmosphere as a result of
various chemical reactions from precursor emissions of nitrogen oxides,
sulfur oxides, volatile organic compounds, and ammonia (secondary
PM2.5).\4\
---------------------------------------------------------------------------
\4\ 80 FR 15340, 15342 (March 23, 2015).
---------------------------------------------------------------------------
B. San Joaquin Valley Designations, Classifications, and Attainment
Dates for 1997 PM2.5 NAAQS
Following promulgation of a new or revised NAAQS, the EPA is
required under CAA section 107(d) to designate areas throughout the
nation as attaining or not attaining the NAAQS. On January 5, 2005, the
EPA published initial air quality designations for the 1997 annual and
24-hour PM2.5 NAAQS, using air quality monitoring data for
the three-year periods of 2001-2003 and 2002-2004.\5\ These
designations became effective April 5, 2005.\6\ The EPA designated the
San Joaquin Valley area as nonattainment for both the 1997 annual
PM2.5 standards and the 1997 24-hour PM2.5
standards.\7\
---------------------------------------------------------------------------
\5\ 70 FR 944 (January 5, 2005).
\6\ Id.
\7\ 40 CFR 81.305. The 2001-2003 design values for the San
Joaquin Valley were 21.8 [mu]g/m\3\ for the annual standard and 82
[mu]g/m\3\ for the 24-hour standard. See EPA design value workbook
dated August 28, 2014, worksheets ``Table 3a'' and ``Table 3b.''
---------------------------------------------------------------------------
The San Joaquin Valley PM2.5 nonattainment area
encompasses over 23,000 square miles and includes all or part of eight
counties: San Joaquin, Stanislaus, Merced, Madera, Fresno, Tulare,
Kings, and the valley portion of Kern.\8\ The area is home to four
million people and is the nation's leading agricultural region.
Stretching over 250 miles from north to south and averaging 80 miles
wide, it is partially enclosed by the Coast Mountain range to the west,
the Tehachapi Mountains to the south, and the Sierra Nevada range to
the east.
---------------------------------------------------------------------------
\8\ For a precise description of the geographic boundaries of
the San Joaquin Valley PM2.5 nonattainment area, see 40
CFR 81.305.
---------------------------------------------------------------------------
Under state law, the California Air Resources Board (CARB or
``State'') is the Governor's designee for adoption and submittal of the
state implementation plan (SIP) and SIP revisions to the EPA in
compliance with CAA requirements. CARB is also generally responsible
under state law for the regulation of mobile emission sources. Local
air pollution control districts are responsible for regulation of
stationary emission sources. In the San Joaquin Valley, regional air
quality plans are developed by the San Joaquin Valley Unified Air
Pollution Control District (SJVUAPCD or ``District'') with input from
CARB and typically rely on both mobile source control measures for
which CARB is responsible and stationary source control measures for
which the District is responsible. Once the District adopts a regional
air quality plan, the plan is submitted to CARB for adoption as part of
the California SIP and submittal to the EPA.
Between 2007 and 2011, California made six SIP submissions to
address nonattainment area planning requirements for the 1997
PM2.5 NAAQS in the San Joaquin Valley.\9\ We refer to these
submissions collectively as the ``2008 PM2.5 Plan.'' On
November 9, 2011, the EPA approved all elements of the 2008
PM2.5 Plan except for the contingency measures, which the
EPA disapproved.\10\ As part of that action and pursuant to CAA section
172(a)(2)(A), the EPA granted California's request for an extension of
the attainment date for the San Joaquin Valley area to April 5,
2015.\11\
---------------------------------------------------------------------------
\9\ 76 FR 69896 at n. 2 (November 9, 2011).
\10\ Id. at 69924.
\11\ Id. Under CAA section 172(a)(2)(A), the attainment date for
a nonattainment area is ``the date by which attainment can be
achieved as expeditiously as practicable, but no later than five
years from the date such area was designated nonattainment,'' except
that EPA may extend the attainment date as appropriate for a period
no greater than ten years from the date of designation as
nonattainment, considering the severity of nonattainment and the
availability and feasibility of pollution control measures. CAA
section 172(a)(2)(A).
---------------------------------------------------------------------------
A 2013 court decision by the U.S. Court of Appeals for the D.C.
Circuit (``D.C. Circuit'') in Natural Resources Defense Council v. EPA
concluded that the EPA erred in implementing the 1997 PM2.5
standards solely pursuant to the general implementation requirements of
subpart 1, without also considering the requirements specific to
PM10 nonattainment areas in subpart 4, part D of title I of
the CAA.\12\ Consistent with the NRDC decision, on June 2, 2014, the
EPA classified all areas designated nonattainment for the 1997 or the
2006 PM2.5 standards as ``Moderate'' nonattainment areas
under subpart 4.\13\ Because this rulemaking did not affect any action
that the EPA had previously taken under section 110(k) of the Act on a
SIP for a PM2.5 nonattainment area, the April 5, 2015
attainment date that the EPA had approved for the San Joaquin Valley
area in November 2011 remained in effect.\14\
---------------------------------------------------------------------------
\12\ Natural Resources Defense Council v. EPA, 706 F.3d 428
(D.C. Cir. 2013) (``NRDC'').
\13\ 79 FR 31566 (June 2, 2014). As part of this rulemaking, EPA
established a December 31, 2014 deadline for states to submit
attainment-related and nonattainment new source review SIP elements
required for PM2.5 nonattainment areas pursuant to
subpart 4. Id.
\14\ Id. at 31569.
---------------------------------------------------------------------------
On April 7, 2015, the EPA reclassified the San Joaquin Valley area
as a ``Serious'' PM2.5 nonattainment area under subpart 4,
based on the EPA's determination that the area could not practicably
attain the 1997 PM2.5 standards by the April 5, 2015
attainment date.\15\ This reclassification was based upon the EPA's
evaluation of ambient air quality data from the 2003-2014 period,
including the 2012-2014 design value, which indicated that it was not
practicable for certain monitoring sites within the San Joaquin Valley
area to show PM2.5 design values at or below the level of
the 1997 PM2.5 NAAQS by April 5, 2015.\16\
---------------------------------------------------------------------------
\15\ 80 FR 18528 (April 7, 2015).
\16\ Id. at 18529; see also proposed rule, 80 FR 1482 (January
12, 2015). Air quality data for 2012-2014 indicated that the highest
monitors in the San Joaquin Valley area had design values of 19.7
[mu]g/m\3\ for the annual standard and 71 [mu]g/m\3\ for the 24-hour
standard.
---------------------------------------------------------------------------
As a consequence of reclassification as a Serious PM2.5
nonattainment area, the San Joaquin Valley area became subject to a new
attainment date under CAA section 188(c)(2) and the requirement to
submit a Serious area plan that satisfies the requirements of part D of
title I of the Act, including the requirements of subpart 4, for the
1997 PM2.5 NAAQS.\17\ Under subpart 4, the attainment date
for an area classified as Serious is as expeditiously as
[[Page 69450]]
practicable, but no later than the end of the tenth calendar year
following designation. As explained in the EPA's final reclassification
action, the Serious area plan for the San Joaquin Valley must include
provisions to assure that the best available control measures for the
control of direct PM2.5 and PM2.5 precursors
shall be implemented no later than 4 years after the area is
reclassified (CAA section 189(b)(1)(B)), and a demonstration (including
air quality modeling) that the plan provides for attainment as
expeditiously as practicable but no later than December 31, 2015, which
is the latest permissible attainment date under CAA section
188(c)(2).\18\
---------------------------------------------------------------------------
\17\ 80 FR 18258 at 18530-18532.
\18\ Id.
---------------------------------------------------------------------------
Given the December 31, 2015 outermost attainment deadline for the
San Joaquin Valley area under section 188(c)(2), the EPA noted its
expectation that the State would adopt and submit a Serious area plan
for the San Joaquin Valley well before the statutory SIP submission
deadlines in CAA section 189(b)(2).\19\ The EPA also noted that, in
light of the available ambient air quality data and the short amount of
time available before the December 31, 2015 attainment date, California
could choose to submit a request for an extension of the Serious area
attainment date pursuant to CAA section 188(e) simultaneously with its
submission of a Serious area plan for the area.\20\
---------------------------------------------------------------------------
\19\ Id. at 18531.
\20\ Id.
---------------------------------------------------------------------------
California submitted its 1997 PM2.5 Serious area plan
for the San Joaquin Valley in two submittals dated June 25, 2015 and
August 13, 2015, including a request under section 188(e) to extend the
attainment date for the 1997 24-hour PM2.5 NAAQS by three
years (to December 31, 2018) and to extend the attainment date for the
1997 annual PM2.5 NAAQS by five years (to December 31,
2020). The EPA proposed to approve most of the San Joaquin Valley 1997
PM2.5 Serious area plan, to conditionally approve the Plan's
quantitative milestones, to disapprove the plan's contingency measures,
and to grant the requested attainment date extensions.\21\ We received
adverse comments on our proposal on several aspects of the plan and its
control measures. Upon further evaluation of the plan and after
consideration of the comments, the EPA decided it could no longer
support an action to extend the attainment date for the San Joaquin
Valley Serious PM2.5 nonattainment area for the 1997
PM2.5 NAAQS.\22\
---------------------------------------------------------------------------
\21\ 81 FR 6936 (February 9, 2016).
\22\ See U.S. EPA, Final rule, ``Denial of Request for Extension
of Attainment Date for 1997 PM2.5 NAAQS; California; San
Joaquin Valley Serious Nonattainment Area,'' to be published in the
same edition of the Federal Register as this proposed rule, and U.S.
EPA Fact Sheet, ``San Joaquin Valley Fine Particulate Matter,'' June
29, 2016.
---------------------------------------------------------------------------
Since the EPA has not approved the requested attainment date
extensions, the applicable attainment date remains December 31, 2015
for the San Joaquin Valley with respect to the 1997 PM2.5
NAAQS. As discussed in section II of this proposed rule, the EPA must
determine, based on air quality data as of the attainment date, whether
an area attained the applicable NAAQS by its attainment date.
II. Proposed Determination and Consequences
A. Applicable Statutory and Regulatory Provisions
Sections 179(c)(1) and 188(b)(2) of the CAA require the EPA to
determine whether a PM2.5 nonattainment area attained the
applicable PM2.5 standards by the applicable attainment
date, based on the area's air quality as of the attainment date.
A determination of whether an area's air quality meets the
PM2.5 standards is generally based upon the most recent
three years of complete, quality-assured data gathered at established
State and Local Air Monitoring Stations (SLAMS) in a nonattainment area
and entered into the EPA's Air Quality System (AQS) database. Data from
ambient air monitors operated by state/local agencies in compliance
with the EPA monitoring requirements must be submitted to AQS.
Monitoring agencies annually certify that these data are accurate to
the best of their knowledge. Accordingly, the EPA relies primarily on
data in AQS when determining the attainment status of areas. See 40 CFR
50.7; 40 CFR part 50, Appendix L; 40 CFR part 53; 40 CFR part 58, and
40 CFR part 58, Appendices A, C, D, and E. All data are reviewed to
determine the area's air quality status in accordance with 40 CFR part
50, Appendix N.
Under EPA regulations in 40 CFR part 50, Sec. 50.7 and in
accordance with Appendix N, the 1997 annual PM2.5 standards
are met when the design value is less than or equal to 15.0 [micro]g/
m\3\ (based on the rounding convention in 40 CFR part 50, Appendix N)
at each eligible monitoring site within the area.\23\ Data completeness
requirements for a given year are met when at least 75 percent of the
scheduled sampling days for each quarter have valid data.
---------------------------------------------------------------------------
\23\ The annual PM2.5 standard design value is the 3-
year average of annual mean concentration, and the 1997 annual
PM2.5 NAAQS are met when the annual standard design value
at each eligible monitoring site is less than or equal to 15.0
[micro]g/m\3\.
---------------------------------------------------------------------------
Under EPA regulations in 40 CFR part 50, section 50.7 and in
accordance with Appendix N, the 1997 24-hour PM2.5 standards
are met when the design value is less than or equal to 65 [micro]g/m\3\
(based on the rounding convention in 40 CFR part 50, Appendix N) at
each eligible monitoring site within the area.\24\ Data completeness
requirements for a given year are met when at least 75 percent of the
scheduled sampling days for each quarter have valid data.
---------------------------------------------------------------------------
\24\ The 24-hour PM2.5 standard design value is the
3-year average of annual 98th percentile 24-hour average values
recorded at each eligible monitoring site, and the 1997 24-hour
PM2.5 NAAQS are met when the 24-hour standard design
value at each such monitoring site is less than or equal to 65
[micro]g/m\3\.
---------------------------------------------------------------------------
B. Monitoring Network Considerations
Section 110(a)(2)(B)(i) of the CAA requires states to establish and
operate air monitoring networks to compile data on ambient air quality
for all criteria pollutants. Our monitoring requirements are specified
by regulation in 40 CFR part 58. These requirements are applicable to
state, and where delegated, local air monitoring agencies that operate
criteria pollutant monitors. Our regulations in 40 CFR part 58
establish specific requirements for operating air quality surveillance
networks to measure ambient concentrations of PM2.5,
including requirements for measurement methods, network design, quality
assurance procedures, and in the case of large urban areas, the minimum
number of monitoring sites designated as SLAMS.
In section 4.7 of Appendix D to 40 CFR part 58, the EPA specifies
minimum monitoring requirements for PM2.5 to operate at
SLAMS. SLAMS produce data that are eligible for comparison with the
NAAQS, and therefore, the monitor must be an approved federal reference
method (FRM), federal equivalent method (FEM), or approved regional
method (ARM). The minimum number of SLAMS required is described in
section 4.7.1, and can be met by either filter-based or continuous FRMs
or FEMs. The monitoring regulations also provide that each core-based
statistical area must operate a minimum number of PM2.5
continuous monitors (section 4.7.2); however, this requirement can be
met by either an FEM or a non-FEM continuous monitor, and the
continuous monitors can be located with other SLAMS or at a different
location.
[[Page 69451]]
Consequently, the monitoring requirements for PM2.5 can be
met with filter-based FRMs/FEMs, continuous FEMs, continuous non-FEMs,
or a combination of monitors at each required SLAMS.
Under 40 CFR 58.10, states are required to submit Annual Network
Plans for ambient air monitoring networks for approval by the EPA.
Within the San Joaquin Valley, CARB and the District are the agencies
responsible for assuring that the area meets air quality monitoring
requirements. The District submits annual monitoring network plans to
the EPA that describe the various monitoring sites operated by the
District as well as those operated by CARB within the San Joaquin
Valley. These plans discuss the status of the air monitoring network,
as required under 40 CFR 58.10. The most recent plan submitted by the
District is the 2015 Air Monitoring Network Plan, dated August 28,
2015. The EPA regularly reviews these Annual Network Plans for
compliance with the applicable reporting requirements in 40 CFR part
58. On December 28, 2015, the EPA approved those portions of the 2015
Air Monitoring Network Plan that pertain to the adequacy of the network
for PM2.5 monitoring purposes.\25\
---------------------------------------------------------------------------
\25\ Letter dated December 28, 2015, from Meredith Kurpius,
Manager, EPA Region 9, Air Quality Analysis Office, to Sheraz Gill,
Director of Strategies and Incentives, SJVUAPCD.
---------------------------------------------------------------------------
During the 2013-2015 period, PM2.5 ambient concentration
data that is eligible for use in determining whether an area has
attained the PM2.5 NAAQS were collected at a total of 17
sites within the San Joaquin Valley: four sites in Fresno County; three
sites in Kern County; two sites each in Kings, Merced, San Joaquin, and
Stanislaus counties; and one site each in Madera and Tulare counties.
The District operates 10 of these sites while CARB operates seven of
the sites. Fourteen of the sites are designated SLAMS for
PM2.5. Three of the sites are designated as special purpose
monitors (i.e., the Merced (Coffee Street), Tranquility, and Hanford
sites), but the PM2.5 data collected there are eligible for
use in determining PM2.5 NAAQS compliance due to the
duration of monitoring at the site and the use of FRM or FEM monitors
consistent with EPA quality assurance requirements and siting
criteria.\26\ The primary monitors are FRMs at 11 of the 17 sites and
beta attenuation monitor FEMs at six of the 17 sites.
---------------------------------------------------------------------------
\26\ There are a number of other PM2.5 monitoring
sites within the valley, including other sites operated by the
District, the National Park Service, and certain Indian tribes, but
the data collected from these sites are non-regulatory and not
eligible for use in determining whether the San Joaquin Valley has
attained the PM2.5 NAAQS.
---------------------------------------------------------------------------
Based on our review of the PM2.5 monitoring network as
summarized above, we find that monitoring network in the San Joaquin
Valley is adequate for the purpose of collecting ambient
PM2.5 concentration data for use in determining whether the
San Joaquin Valley attained the 1997 PM2.5 NAAQS by the
December 31, 2015 attainment date.
C. Data Considerations and Proposed Determination
Under 40 CFR 58.15, monitoring agencies must certify, on an annual
basis, data collected at all SLAMS and at all FRM, FEM, and ARM SPM
stations that meet EPA quality assurance requirements. In doing so,
monitoring agencies must certify that the previous year of ambient
concentration and quality assurance data are completely submitted to
AQS and that the ambient concentration data are accurate to the best of
her or his knowledge. CARB annually certifies that the data the agency
submits to AQS are quality assured, including data collected by CARB at
monitoring sites in the San Joaquin Valley.\27\ SJVUAPCD does the same
for data submitted to AQS from monitoring sites operated by the
District.\28\
---------------------------------------------------------------------------
\27\ See, e.g., letter from Ravi Ramalingam, Chief, Consumer
Products and Air Quality Assessment Branch, CARB, to Elizabeth
Adams, Acting Director, Air Division, EPA Region 9, certifying
calendar year 2015 ambient air quality data and quality assurance
data, dated May 10, 2016.
\28\ See, e.g., letter from Jon Klassen, Program Manager,
SJVUAPCD, letter to Deborah Jordan, Director, Air Division, EPA
Region 9, certifying calendar year 2015 ambient air quality data and
quality assurance data, dated May 9, 2016.
---------------------------------------------------------------------------
As noted above, CAA sections 179(c)(1) and 188(b)(2) require the
EPA to determine whether a PM2.5 nonattainment area attained
the applicable PM2.5 standards by the applicable attainment
date, based on the area's air quality ``as of the attainment date.''
For the San Joaquin Valley, for reasons discussed above, the applicable
attainment date is December 31, 2015 with respect to the 1997
PM2.5 NAAQS. Because determinations of PM2.5
NAAQS compliance, in accordance with 40 CFR part 50, Appendix N, are
based on three calendar years of data, to determine the San Joaquin
Valley's air quality as of December 31, 2015, we must review the data
collected during the three-year period immediately preceding December
31, 2015, i.e., January 1, 2013-December 31, 2015.
Thus, we verified that the data for the 2013-2015 period have been
certified by the relevant monitoring agencies, and then we reviewed the
data for completeness. We note above the most recent annual data
certifications from CARB and the District. With respect to
completeness, we determined that the data collected by CARB and the
District meet the quarterly completeness criterion for all 12 quarters
of the three-year period at most of the PM2.5 monitoring
sites in the San Joaquin Valley.
More specifically, among the 17 PM2.5 monitoring sites
from which regulatory data are available, the data from four of the
sites did not meet the 75% completeness criterion (for each quarter);
however, the data from all but one site (Bakersfield--Golden State
Highway) are sufficient nonetheless to produce a valid design value for
either the annual PM2.5 NAAQS or the 24-hour
PM2.5 NAAQS pursuant to the rules governing design value
validity in 40 CFR part 50, Appendix N, sections 4.1 and 4.2. We note
that monitors with incomplete data in one or more quarters may still
produce valid design values if the conditions for applying one of the
EPA's data substitution tests are met.\29\
---------------------------------------------------------------------------
\29\ See 40 CFR part 50, Appendix N, section 4.1(b) for the
annual PM2.5 NAAQS and section 4.2(b) for the 24-hour
PM2.5 NAAQS. Each year the EPA produces a workbook
identifying PM2.5 monitors with valid design values
taking into account the data substitution tests set forth in 40 CFR
part 50, Appendix N, section 4 where appropriate. The workbook
design values reflect the concentration data input to AQS, but the
design values calculated therein differ for some monitors from the
design values calculated by AQS because at this time only the
workbook design values accurately accounts for the two data
substitution tests set forth in 40 CFR part 50, Appendix N, section
4.0.
---------------------------------------------------------------------------
Table 1 and Table 2 show the annual and 24-hour PM2.5
design values, respectively, at each of the 17 monitoring sites within
the San Joaquin Valley nonattainment area for the relevant three-year
period (2013-2015). The tables show that the annual PM2.5
design values for the 2013-2015 period are greater than 15.0 [micro]g/
m\3\ at eight of the sites and that the 24-hour PM2.5 design
values are greater than 65 [micro]g/m\3\ at four of the sites.
[[Page 69452]]
Table 1--2013-2015 Annual PM2.5 Design Values for the San Joaquin Valley Nonattainment Area
----------------------------------------------------------------------------------------------------------------
Annual Mean ([micro]g/m\3\) 2013-2015
--------------------------------------- Annual
design
General location Site (AQS ID) values
2013 2014 2015 ([micro]g/
m\3\)
----------------------------------------------------------------------------------------------------------------
Fresno County:
Fresno-Pacific.......................... 06-019-5025 15.9 13.8 14.1 14.6
Fresno--Garland......................... 06-019-0011 16.8 15.1 14.4 15.4
Clovis.................................. 06-019-5001 15.9 14.8 15.0 15.2
Tranquility \a\......................... 06-019-2009 8.3 Inc 10.0 8.7
Kern County:
Bakersfield--Planz Road................. 06-029-0016 22.8 21.6 17.9 20.8
Bakersfield--California Ave............. 06-029-0014 20.0 18.6 16.3 18.3
Bakersfield--Golden State Highway....... 06-029-0010 Inc Inc 16.7 Inv
Kings County:
Corcoran \a\ \b\........................ 06-031-0004 15.6 15.4 Inc 22.2
Hanford................................. 06-031-1004 18.2 17.5 16.6 17.4
Madera County:
Madera--Avenue 14....................... 06-039-2010 17.8 14.0 13.8 15.2
Merced County:
Merced--M Street........................ 06-047-2510 13.5 11.2 12.6 12.5
Merced--Coffee.......................... 06-047-0003 13.3 10.8 12.8 12.3
San Joaquin County:
Stockton................................ 06-077-1002 17.7 12.1 12.8 14.2
Manteca................................. 06-077-2010 11.7 9.8 12.6 11.4
Stanislaus County:
Modesto................................. 06-099-0005 14.5 11.4 Inc Inv
Turlock................................. 06-099-0006 15.1 12.3 14.4 13.9
Tulare County:
Visalia................................. 06-107-2002 18.9 17.9 16.1 17.6
----------------------------------------------------------------------------------------------------------------
Notes: Inc = Incomplete data. Inv = Invalid design value due to incomplete data. Design values shown in bold
type do not meet the applicable NAAQS.
Source: EPA, AQS Design Value Report, Report Request ID: 1463864, July 15, 2016, except as otherwise noted.
\a\ Source: EPA, design value workbook dated July 29, 2016, worksheet ``Table 5. PM2.5 Site Listing, 2013-
2015,'' column S.
\b\ The 2015 design value site (Corcoran-Patterson) is based on concentration data from January 1, 2013 to
February 6, 2015. Data from February 7, 2015 to December 31, 2015 are not available due to a fire that
destroyed the site. Based on design value calculation methodologies described in 40 CFR part 50, Appendix N,
section 4.1(b), the annual design value for Corcoran-Patterson is considered valid despite the missing 2015
data. The second highest 2013-2015 concentration (annual PM2.5 design value of 20.8 [micro]g/m\3\) at
Bakersfield-Planz includes data measured for three years (January 1, 2013-December 31, 2015).
Table 2--2013-2015 24-Hour PM2.5 Design Values for the San Joaquin Valley Nonattainment Area
----------------------------------------------------------------------------------------------------------------
98th Percentile ([micro]g/m\3\) 2013-2015
--------------------------------------- 24-Hour
design
General location Site (AQS ID) values
2013 2014 2015 ([micro]g/
m\3\)
----------------------------------------------------------------------------------------------------------------
Fresno County:
Fresno--Pacific......................... 06-019--5025 71.6 61.8 42.0 58
Fresno-Garland.......................... 06-019-0011 63.8 66.7 52.0 61
Clovis.................................. 06-019-5001 56.2 64.5 45.7 55
Tranquility \a\......................... 06-019-2009 35.7 Inc 35.8 34
Kern County:
Bakersfield--Planz Road................. 06-029-0016 96.7 76.7 56.5 77
Bakersfield--California Ave............. 06-029-0014 71.8 79.9 57.2 70
Bakersfield--Golden State Highway \a\... 06-029-0010 Inc 107.2 51.5 Inv
Kings County:
Corcoran \b\............................ 06-031-0004 66.0 71.0 99.2 79
Hanford................................. 06-031-1004 67.6 81.9 51.4 67
Madera County:
Madera--Avenue 14....................... 06-039-2010 54.6 56.0 43.7 51
Merced County:
Merced--M Street........................ 06-047-2510 67.3 45.9 39.0 51
Merced--Coffee.......................... 06-047-0003 42.3 43.8 40.3 42
San Joaquin County:
Manteca................................. 06-077-2010 40.2 40.0 42.7 41
Stockton................................ 06-077-1002 56.3 44.5 39.1 47
Stanislaus County:
Modesto................................. 06-099-0005 56.4 49.5 30.8 46
Turlock................................. 06-099-0006 55.4 51.2 47.3 51
Tulare County:
[[Page 69453]]
Visalia................................. 06-107-2002 62.5 75.4 45.8 61
----------------------------------------------------------------------------------------------------------------
Notes: Inc = Incomplete data. Inv = Invalid design value due to incomplete data. Design values shown in bold
type do not meet the applicable NAAQS.
Source: EPA, AQS Design Value Report, Report Request ID: 1463864, July 15, 2016, except as otherwise noted.
\a\ Source: EPA, design value workbook dated July 29, 2016, worksheet ``Table 5. PM2.5 Site Listing, 2013-
2015,'' column Z.
\b\ The 2015 design value site (Corcoran-Patterson) is based on concentration data from January 1, 2013 to
February 6, 2015. Data from February 7, 2015 to December 31, 2015 are not available due to a fire that
destroyed the site. Based on design value calculation methodologies described in 40 CFR part 50, Appendix N,
section 4.2(b), the 24-hour design value for Corcoran-Patterson is considered valid despite the missing 2015
data. The second highest 2013-2015 concentration (24-hour PM2.5 design value of 77 [micro]g/m\3\) at
Bakersfield--Planz includes data measured for three years (January 1, 2013-December 31, 2015).
The data in Tables 1 and 2 show that a number of sites in central
and southern San Joaquin Valley failed to attain the 1997 annual
PM2.5 NAAQS by December 31, 2015 and that the geographic
extent of failure to attain the 1997 24-hour PM2.5 NAAQS was
more limited than for the annual standard in that only sites in
southwestern San Joaquin Valley failed to attain the 24-hour standard.
The 2015 annual design value site, i.e., the site with the highest
design value based on 2013-2015 data, is the Corcoran site with a 2015
annual PM2.5 design value of 22.2 [micro]g/m\3\. With
respect to the 24-hour average, the 2015 design value site is the
Corcoran site with a 24-hour PM2.5 design value of 79
[micro]g/m\3\.
For an area to attain the 1997 PM2.5 NAAQS by December
31, 2015, the 2015 design value (reflecting data from 2013-2015) at
each eligible monitoring site must be equal to or less than 15.0
[micro]g/m\3\ for the annual standard and 65 [micro]g/m\3\ for the 24-
hour standard. Tables 1 and 2 show that the 2015 design values at a
number of sites in the San Joaquin Valley are greater than those
values. Therefore, based on quality-assured and certified data for
2013-2015, we are proposing to determine that the San Joaquin Valley
failed to attain the 1997 annual and 24-hour PM2.5 standards
by the December 31, 2015 attainment date.
Lastly, we note that, under our regulations at 40 CFR 50.14, a
monitoring agency may request the EPA to exclude data showing
exceedances or violations of the standard that are directly due to an
exceptional event from use in determinations by demonstrating that such
event caused a specific air pollution concentration at a particular air
quality monitoring location. A monitoring agency notifies the EPA of
its intent to request exclusion of concentrations by placing a ``flag''
in the appropriate field for the data of concern in AQS.
For PM2.5 ambient data collected from 2013-2015, the
District ``flagged'' one 24-hour concentration at the Bakersfield
(Planz Road) site and two 24-hour concentrations at the Bakersfield
(California Avenue) site due to high winds. The District also flagged
twenty-four 24-hour concentrations at each of the Madera and Merced
(Coffee Avenue) sites due to wildfire.\30\
---------------------------------------------------------------------------
\30\ EPA, AQS Raw Data Qualifier Report, Report Request ED:
1464417, July 18, 2016.
---------------------------------------------------------------------------
The State has not requested concurrence on the flagged data, and
thus the data are not excluded from the set of data used to determine
whether the standard was attained. However, even if all of the flagged
data were to be excluded, i.e., even if the EPA had concurred on the
data as qualifying as exceptional events, the design values reported in
Tables 1 and 2, though slightly lower at certain sites, would remain
well above the NAAQS.\31\
---------------------------------------------------------------------------
\31\ EPA, AQS Design Value Report, Report Request ED: 1463865,
July 15, 2016.
---------------------------------------------------------------------------
For instance, the 2015 annual PM2.5 design value at the
Bakersfield (Planz Road) monitoring site would be 20.4 [mu]g/m\3\
instead of 20.8 [mu]g/m\3\ if all of the flagged data were excluded.
Thus, it would still fail to attain the applicable standard of 15.0
[mu]g/m\3\. Similarly, the 2015 24-hour PM2.5 design value
at the same site would be 72 [mu]g/m\3\ instead of 77 [mu]g/m\3\ if all
of the flagged data were excluded, thus also failing to attain the
applicable standard of 65 [mu]g/m\3\. Furthermore, several additional
sites, for which the District has not flagged exceptional events,
exceed the 1997 PM2.5 NAAQS based on 2015 annual
PM2.5 design values (i.e., Fresno-Garland, Clovis, Corcoran,
Hanford, and Visalia) and 2015 24-hour design values (i.e., Corcoran
and Hanford).
D. Consequences for Serious PM2.5 Nonattainment Area Failing To Attain
Standards by Attainment Date
The consequences for a Serious PM2.5 nonattainment area
for failing to attain the standards by the applicable attainment date
are set forth in CAA sections 179(d) and 189(d). Under section 179(d),
a state must submit a SIP revision for the area meeting the
requirements of CAA section 110 and 172, the latter of which requires,
among other elements, a demonstration of attainment and reasonable
further progress, and contingency measures. CAA section 189(d) requires
that the SIP revision must provide for attainment of the standards and,
from the date of the SIP submittal until attainment, for an annual
reduction in the emissions of PM2.5 or a PM2.5
plan precursor pollutant within the area of not less than five percent
of the amount of such emissions as reported in the most recent
inventory prepared for such area.\32\ The requirement for a new
attainment demonstration under CAA section 189(d) also triggers the
requirement for the SIP revision for quantitative milestones under
section 189(c) that are to be achieved every three years until
redesignation to attainment.
---------------------------------------------------------------------------
\32\ 81 FR 58010 at 58100, 58158 (August 24, 2016). The EPA
defines PM2.5 plan precursor as those PM2.5
precursors required to be regulated in the applicable attainment
plan and/or nonattainment new source review program. 81 FR 58010 at
58152.
---------------------------------------------------------------------------
The new attainment date is set by CAA section 179(d)(3), which
relies upon section 172(a)(2) to establish a new attainment date but
with a different starting point than provided in section 172(a)(2).
Under section 179(d)(3), the new attainment date is the date by which
attainment can be achieved as expeditiously as practicable, but no
later than five years from the date of the final determination of
failure to attain, except that the EPA may extend the attainment
[[Page 69454]]
date for a period no greater than 10 years from the final
determination, considering the severity of nonattainment and the
availability and feasibility of pollution control measures. Lastly,
section 179(d) requires that the state submit the required SIP revision
within 12 months after the applicable attainment date. In this case, if
the EPA finalizes the proposed rule, then the State of California will
be required to submit a SIP revision that complies with sections 179(d)
and 189(d) within 12 months of December 31, 2015, i.e., by December 31,
2016.
III. Proposed Action and Request for Public Comment
Under CAA sections 179(c)(1) and 188(b)(2), the EPA proposes to
determine that the San Joaquin Valley ``Serious'' PM2.5
nonattainment area has failed to attain the 1997 annual and 24-hour
PM2.5 standards by the applicable attainment date of
December 31, 2015. If finalized, the State of California will be
required under CAA sections 179(d) and 189(d) to submit a revision to
the SIP for the San Joaquin Valley that, among other elements,
demonstrates expeditious attainment of the standards within the time
period provided under CAA section 179(d) and that provides for annual
reduction in the emissions of PM2.5 or a PM2.5
plan precursor pollutant within the area of not less than five percent
until attainment. The SIP revision required under CAA sections 179(d)
and 189(d) would be due for submittal to the EPA no later than December
31, 2016.
The EPA is soliciting public comments on the issues discussed in
this document. We will accept comments from the public on this proposal
for the next 30 days. We will consider these comments before taking
final action.
IV. Statutory and Executive Order Reviews
This proposed action in and of itself establishes no new
requirements; it merely documents that air quality in the San Joaquin
Valley did not meet the 1997 PM2.5 standards by the CAA
deadline. For that reason, this proposed action:
Is not a ``significant regulatory action'' subject to
review by the Office of Management and Budget under Executive Order
12866 (58 FR 51735, October 4, 1993);
Does not impose an information collection burden under the
provisions of the Paperwork Reduction Act (44 U.S.C. 3501 et seq.);
Is certified as not having a significant economic impact
on a substantial number of small entities under the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.);
Does not contain any unfunded mandate or significantly or
uniquely affect small governments, as described in the Unfunded
Mandates Reform Act of 1995 (Pub. L. 104-4);
Does not have Federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999);
Is not an economically significant regulatory action based
on health or safety risks subject to Executive Order 13045 (62 FR
19885, April 23, 1997);
Is not a significant regulatory action subject to
Executive Order 13211 (66 FR 28355, May 22, 2001);
Is not subject to requirements of section 12(d) of the
National Technology Transfer and Advancement Act of 1995 (15 U.S.C. 272
note) because application of those requirements would be inconsistent
with the CAA; and
Does not provide the EPA with the discretionary authority
to address disproportionate human health or environmental effects with
practical, appropriate, and legally permissible methods under Executive
Order 12898 (59 FR 7629, February 16, 1994).
In addition, this proposed action does not have Tribal implications
as specified by Executive Order 13175 (65 FR 67249, November 9, 2000),
because the SIP obligations discussed herein do not apply to Indian
Tribes and thus this proposed action will not impose substantial direct
costs on Tribal governments or preempt Tribal law. Nonetheless, the EPA
has notified the Tribes within the San Joaquin Valley PM2.5
nonattainment area of the proposed action.
List of Subjects in 40 CFR Part 52
Environmental protection, Air pollution control, Ammonia,
Incorporation by reference, Intergovernmental relations, Nitrogen
dioxide, Particulate matter, Reporting and recordkeeping requirements,
Sulfur oxides, Volatile organic compounds.
Dated: September 23, 2016.
Alexis Strauss,
Acting Regional Administrator, Region IX.
[FR Doc. 2016-24084 Filed 10-5-16; 8:45 am]
BILLING CODE 6560-50-P