Source: https://www.federalregister.gov/documents/2020/03/20/2020-05671/approval-and-promulgation-of-air-quality-implementation-plans-state-of-montana-columbia-falls
Timestamp: 2020-04-01 03:03:21
Document Index: 622728858

Matched Legal Cases: ['art 1', 'art 4', 'arts 51', 'arts 51', 'art 50', 'art 50', 'art 1', 'art 4', 'art 1', 'art 58', 'art 58', 'art 4', 'art 58', 'art 93', 'art 93', 'art 93', 'art 93']

Federal Register :: Approval and Promulgation of Air Quality Implementation Plans; State of Montana; Columbia Falls, Kalispell and Libby PM10
16029-16038 (10 pages)
FRL-10006-48-Region 8
A. Description of the Columbia Falls NAA
B. Description of the Libby NAA
C. Description of the Kalispell NAA
A. CAA Requirements for Redesignation of NAAs
B. The LMP Option for PM 10 NAAs
III. Review of Montana's Submittal Addressing the Requirements for Redesignation and Limited Maintenance Plans
A. Have the Columbia Falls, Kalispell and Libby NAAs attained the applicable NAAQS?
B. Do the Columbia Falls, Kalispell, and Libby NAA have a fully approved SIP under CAA Section 110(k)?
3. Subpart 1, Section 172(c)
4. Section 172(c)(3)—Emissions Inventory Section
5. Section 172(c)(5)—NSR
6. Section 172(c)(7)—Compliance With CAA Section 110(a)(2): Air Quality Monitoring Requirements
7. Section 172(c)(9)—Contingency Measures
8. Part D Subpart 4
1. Permanent and Enforceable Emission Reductions in the Columbia Falls NAA
2. Permanent and Enforceable Emission Reductions in the Kalispell NAA
3. Permanent and Enforceable Emission Reductions in the Libby NAA
E. Do the areas have a fully approved maintenance plan pursuant to Section 175A of the CAA?
F. Has the state demonstrated that the Columbia Falls, Kalispell, and Libby NAAs qualify for the LMP option?
I. Does the plan meet the CAA requirements for contingency provisions for maintenance plans?
J. Has the state met transportation and general conformity requirements?
https://www.federalregister.gov/d/2020-05671 https://www.federalregister.gov/d/2020-05671
The Environmental Protection Agency (EPA) is proposing to fully approve three Limited Maintenance Plans (LMPs), submitted by the State of Montana to the EPA on July 23, 2019, for the Columbia Falls, Kalispell and Start Printed Page 16030Libby Moderate nonattainment areas (NAAs) for particulate matter with an aerodynamic diameter less than or equal to a nominal 10 micrometers (PM10) and concurrently redesignate the NAAs to attainment of the 24-hour PM10 National Ambient Air Quality Standard (NAAQS). In order to approve the LMPs and redesignations, the EPA is proposing to determine that the Kalispell and Libby NAAs have attained the 1987 24-hour PM10 NAAQS of 150 µg/m3. This determination is based upon monitored air quality data for the PM10 NAAQS during the years 2016-2018. The EPA is also proposing to approve the Kalispell, Columbia Falls, and Libby LMPs as meeting the appropriate transportation conformity requirements.
Submit your comments, identified by Docket ID No. EPA-R08-OAR-2019-0690 at http://www.regulations.gov. Follow the online instructions for submitting comments. Once submitted, comments cannot be edited or removed from www.regulations.gov 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, the full EPA public comment policy, information about CBI or multimedia submissions, and general guidance on making effective comments, please visit http://www2.epa.gov/​dockets/​commenting-epa-dockets.
Docket: All documents in the docket are listed in the www.regulations.gov index. Although listed in the index, some information is not publicly available, e.g., CBI or other information whose disclosure is restricted by statute. Certain other material, such as copyrighted material, will be publicly available only in hard copy. Publicly available docket materials are available either electronically in www.regulations.gov or in hard copy at the Air and Radiation Division, U.S. Environmental Protection Agency (EPA), Region 8, 1595 Wynkoop Street, Denver, Colorado 80202-1129. The EPA requests that if at all possible, you contact the individual listed in the FOR FURTHER INFORMATION CONTACT section to view the hard copy of the docket. You may view the hard copy of the docket Monday through Friday, 8:00 a.m. to 4:00 p.m., excluding federal holidays.
Kate Gregory, Air and Radiation Division, U.S. Environmental Protection Agency (EPA), Region 8, Mail Code 8P-ARD-QP, 1595 Wynkoop Street, Denver, Colorado 80202-1129, (303) 312-6175, gregory.kate@epa.gov.
The Columbia Falls NAA is one of three NAAs in Flathead County, is rectangularly shaped, and generally encompasses the downtown portion of Columbia Falls and the nearby surrounding areas. Columbia Falls and was originally designated as a Group I area on August 7, 1987, meaning it was likely to violate the PM10 NAAQS, and was subsequently classified as a Moderate NAA for the 1987 24-hour PM10 NAAQS on November 6, 1991. See 56 FR 56694. States containing initial Moderate PM10 NAAs were required to submit, by November 15, 1991, a Moderate NAA State Implementation Plan (SIP) that, among other requirements, implemented Reasonably Available Control Measures (RACM) by December 10, 1993, and demonstrated whether it was practicable to attain the PM10 NAAQS by December 31, 1994. See generally 57 FR 13498 (April 16, 1992); see also 57 FR 18070 (April 28, 1992).
The State of Montana submitted an initial PM10 SIP to the EPA on May 6, 1992, and subsequent submissions on August 26, 1994 and July 18, 1995. The State of Montana's SIP for the Columbia Falls Moderate NAA included, among other things: A comprehensive emissions inventory; RACM; a demonstration that attainment of the PM10 NAAQS would be achieved in Columbia Falls by December 31, 1994; Reasonable Further Progress (RFP) requirements; and control measures that satisfy the contingency measures requirement of section 172(c)(9) of the CAA. The EPA fully approved the Columbia Falls NAA PM10 attainment plan on March 19, 1996 (61 FR 11153).
The Libby PM10 NAA is an irregularly shaped portion of Lincoln County, comprising of the city of Libby, and the surrounding communities. The area was was originally designated as a Group I area on August 7, 1987, meaning it was likely to violate the PM10 NAAQS, and was subsequently classified as a Moderate NAA for the 1987 24-hour PM10 NAAQS on November 6, 1991. See 56 FR 56694.
The State of Montana submitted an initial PM10 SIP to the EPA on November 25, 1991, with revisions and corrections on May 24, 1993 and June 3, 1994. The State of Montana's SIP for the Libby Moderate PM10 NAA included, among other things: A comprehensive emissions inventory; RACM; a demonstration that attainment of the PM10 NAAQS would be achieved in Libby by December 31, 1994; RFP requirements; and control measures that satisfy the contingency measures requirement of section 172(c)(9) of the CAA. The EPA approved the Libby NAA PM10 attainment plan, with the exception of the contingency plan, on August 30, 1994 (59 FR 44627). Revisions to the contingency plan were submitted by Montana on March 15, 1995 and subsequently approved on September 30, 1996 (61 FR 51074).
The Kalispell NAA is one of three NAAs in Flathead County. It is irregularly shaped and generally encompasses the City of Kalispell and the nearby surrounding areas, including the unincorporated community of Evergreen. Kalispell was originally designated as a Group I area on August 7, 1987, meaning it was likely to violate the PM10 NAAQS, and was subsequently classified as a Moderate NAA for the 1987 24-hour PM10 NAAQS on November 6, 1991. See 56 FR 56694.
The State of Montana submitted an initial PM10 SIP to the EPA on November 25, 1991, and submitted three additional submittals between 1991and 1994. The State of Montana's SIP for the Kalispell Moderate NAA included, among other things: A comprehensive emissions inventory; RACM; a demonstration that attainment of the PM10 NAAQS would be achieved in Kalispell by December 31, 1994; RFP requirements; and control measures that satisfy the contingency measures requirement of section 172(c)(9) of the CAA. The EPA fully approved the Kalispell NAA PM10 attainment plan on March 19, 1996 (61 FR 11153).Start Printed Page 16031
NAAs can be redesignated to attainment after the area has measured air quality data showing it has attained the NAAQS and when certain planning requirements are met. Section 107(d)(3)(E) of the CAA, and the General Preamble to Title I provide the criteria for redesignation. See 57 FR 13498 (April 16, 1992). These criteria are further clarified in a policy and guidance memorandum from John Calcagni, Director, Air Quality Management Division, EPA Office of Air Quality Planning and Standards dated September 4, 1992, “Procedures for Processing Requests to Redesignate Areas to Attainment.” [1] The criteria for redesignation are:
On August 9, 2001, the EPA issued guidance on streamlined maintenance plan provisions for certain moderate PM10 NAAs seeking redesignation to attainment (Memo from Lydia Wegman, Director, Air Quality Standards and Strategies Division, entitled “Limited Maintenance Plan Option for Moderate PM10 Nonattainment Areas,” (hereafter the LMP Option memo)).[2] The LMP Option memo contains a statistical demonstration to show that areas meeting certain air quality criteria will, with a high degree of probability, maintain the standard 10 years into the future. Thus, the EPA has already provided the maintenance demonstration for areas meeting the criteria outlined in the LMP Option memo. It follows that future year emission inventories for these areas, and some of the standard analyses to determine transportation conformity with the SIP are no longer necessary.
To qualify for the LMP Option, the area should have attained the 1987 24-hour PM10 NAAQS, based upon the most recent 5 years of air quality data at all monitors in the area, and the 24-hour design value should be at or below the Critical Design Value (CDV). The CDV is a calculated design value that indicates that the area has a low probability (1 in 10) of exceeding the NAAQS in the future. For the purposes of qualifying for the LMP option, a presumptive CDV of 98 µg/m3 is most often employed, but an area may elect to use a site-specific CDV should the average design value be above 98 µg/m3, while demonstrating that the area has a low probability of exceeding the NAAQS in the future. The annual PM10 standard was effectively revoked on December 18, 2006 (71 FR 61143), and as such will not be discussed as a requirement for qualifying for the LMP option. In addition, the area should expect only limited growth in on-road motor vehicle PM10 emissions (including fugitive dust) and should have passed a motor vehicle regional emissions analysis test. The LMP Option memo also identifies core provisions that must be included in the LMP. These provisions include an attainment year emissions inventory, assurance of continued operation of an EPA-approved air quality monitoring network, and contingency provisions.
The transportation conformity rule (40 CFR parts 51 and 93) and the general conformity rule (40 CFR parts 51 and 93) apply to NAAs and maintenance areas covered by an approved maintenance plan. Under either conformity rule, an acceptable method of demonstrating that a federal action conforms to the applicable SIP is to demonstrate that expected emissions from the planned action are consistent with the emissions budget for the area.
While the EPA's LMP Option does not exempt an area from the need to affirm conformity, it explains that the area may demonstrate conformity without submitting an emissions budget. Under the LMP Option, emissions budgets are treated as essentially not constraining for the length of the maintenance period because it is unreasonable to expect that the qualifying areas would experience so much growth in that period that a violation of the PM10 NAAQS would result. For transportation conformity purposes, the EPA would conclude that emissions in these areas need not be capped for the maintenance period; and therefore, a regional emissions analysis would not be required. Similarly, federal actions subject to the general conformity rule could be considered to satisfy the “budget test” specified in 40 CFR 93.158(a)(5)(i)(A) for the same reasons that the budgets are essentially considered not limited.
States must demonstrate that an area has attained the 24-hour PM10 NAAQS through analysis of ambient air quality data from an ambient air monitoring network representing peak PM10 concentrations. The data should be stored in the EPA Air Quality System (AQS) database. On January 31, 2011, the EPA determined that the Columbia Falls NAA attained the PM10 NAAQS (76 FR 5280). Today, the EPA is proposing to determine that the Libby and Kalispell NAAs have attained the PM10 NAAQS based on monitoring data from calendar years 2016-2018. The 24-hour standard is attained when the expected number of days with levels above 150 µg/m3 (averaged over a 3-year period) is less than or equal to one. 40 CFR 50.6(a). Three consecutive years of air quality data are generally necessary to show attainment of the 24-hour and annual standards for PM10. See 40 CFR part 50, appendix K. A complete year of air quality data, as referred to in 40 CFR part 50, appendix K, is comprised of all four calendar quarters with each quarter containing data from at least 75% of the scheduled sampling days.
The Kalispell and Libby NAAs each have one State and Local Air Monitoring Station (SLAMS) monitor operated by the Montana Department of Environmental Quality (MDEQ). Tables 1 and 2 summarize the PM10 data collected from 2014-2018 for the Kalispell and Libby NAAs, respectively. The EPA deems the data collected from these monitors valid, and the data have been submitted by the MDEQ to be included in AQS.Start Printed Page 16032
Table 1—Summary of Maximum 24-hour PM10 Concentrations (μg/m3) for Kalispell 2014-2018
Based on data from Flathead Valley (Soccer Complex) Site, AQS Identification Number (30-029-0049)
2nd maximum concentration
2014 108 89 0 Flathead Valley Soccer Complex.
2015 1 146 139 0 Flathead Valley Soccer Complex.
2016 87 84 0 Flathead Valley Soccer Complex.
20171 154 131 0 Flathead Valley Soccer Complex.
2018 131 99 0 Flathead Valley Soccer Complex.
1 EPA-concurred exceptional events were are excluded from this year.
Table 2—Summary of Maximum 24-hour PM10 Concentrations (μg/m3) for Libby 2014-2018
2014 47 45 0 Courthouse Annex.
2015 1 143 113 0 Courthouse Annex.
2016 58 57 0 Courthouse Annex
2017 1 134 104 0 Courthouse Annex.
2018 112 106 0 Courthouse Annex.
The PM10 concentrations reported at the Kalispell and Libby monitoring sites showed no measured exceedances of the 24-hour PM10 NAAQS from 2014-2018, and as such, the EPA proposes to determine that the Kalispell and Libby Moderate NAAs have attained the standard for the 24-hour PM10 NAAQS.
In order to qualify for redesignation, the SIP for the area must be fully approved under CAA section 110(k) and must satisfy all requirements that apply to the area. Section 189 of the CAA contains requirements and milestones for all initial Moderate NAA SIPs including: (1) Provisions to assure that RACM (including such reductions in emissions from existing sources in the area as may be obtained through the adoption, at a minimum, of Reasonably Available Control Technology—RACT) shall be implemented no later than December 10, 1993; (2) A demonstration (including air quality modeling) that the plan will provide for attainment as expeditiously as practicable by no later than December 31, 1994, or, where the state is seeking an extension of the attainment date under section 188(e), a demonstration that attainment by December 31, 1994, is impracticable and that the plan provides for attainment by the most expeditious alternative date practicable (CAA sections 189(a)(1)(A)); (3) Quantitative milestones which are to be achieved every 3 years and which demonstrate RFP toward attainment by December 31, 1994, (CAA sections 172(c)(2) and 189(c)); and (4) Contingency measures to be implemented if the area fails to make RFP or attain by its attainment deadline. These contingency measures are to take effect without further action by the state or the EPA. (CAA section 172(c)(9)).
The EPA approved the Columbia Falls, Kalispell and Libby Moderate area plans on March 19, 1996, March 19, 1996, and August 30, 1994, respectively; and approved the revised contingency plan for Libby on September 30, 1996. Each plan included RACM, an attainment demonstration, emissions inventory, quantitative milestones, and control and contingency measure requirements. As such, the areas have fully approved NAA SIPs under section 110(k) of the CAA.
Section 107(d)(3)(E) of the CAA requires that a state containing a NAA must meet all applicable requirements under section 110 and Part D of the CAA for an area to be redesignated to attainment. The EPA interprets this to mean that the state must meet all requirements that applied to the area prior to, and at the time of, the submission of a complete redesignation request. The following is a summary of how Montana meets these requirements.
Section 110(a)(2) of the CAA contains general requirements for state implementation plans. These requirements include, but are not limited to, submittal of a SIP that has been adopted by the state after reasonable notice and public hearing; provisions for establishment and operation of appropriate apparatus, methods, systems and procedures necessary to monitor ambient air quality; implementation of a permit program; provisions for Part C—Prevention of Significant Deterioration (PSD) and Part D—New Source Review (NSR) permit programs; criteria for stationary source emission control measures, monitoring and reporting, provisions for modeling; and provisions for public and local agency participation. See the General Preamble for further explanation of these requirements. 57 FR 13498 (April 16, 1992).
For purposes of redesignation, the EPA's review of the Montana SIP shows that the State has satisfied all requirements under section 110(a)(2) of the CAA. Further, in 40 CFR 52.1372, the EPA has approved Montana's plan for the attainment and maintenance of the national standards under section 110.
Part D contains general requirements applicable to all areas designated nonattainment. The general requirements are followed by a series of subparts specific to each pollutant. All PM10 NAAs must meet the general provisions of Subpart 1 and the specific PM10 provisions in Subpart 4, Start Printed Page 16033“Additional Provisions for Particulate Matter Nonattainment Areas.” The following paragraphs discuss these requirements as they apply to the Columbia Falls, Kalispell and Libby NAAs.
Subpart 1, section 172(c) contains general requirements for NAA plans. A thorough discussion of these requirements may be found in the General Preamble. See 57 FR 13538 (April 16, 1992). CAA section 172(c)(2) requires nonattainment plans to provide for RFP. Section 171(1) of the CAA defines RFP as “such annual incremental reductions in emissions of the relevant air pollutant as are required by this part (part D of title I) or may reasonably be required by the Administrator for the purpose of ensuring attainment of the applicable national ambient air quality standard by the applicable date.” Since the EPA is proposing to determine that the Kalispell and Libby NAAs are in attainment of the PM10 NAAQS, we believe that no further showing of RFP or quantitative milestones is necessary.
Section 172(c)(3) of the CAA requires a comprehensive, accurate, current inventory of actual emissions from all sources in the Columbia Falls, Kalispell and Libby PM10 NAAs. Montana included an emissions inventory for the calendar year 2014 with July 23, 2019 submittal of the LMP for the NAAs. The LMP Option memo states that an attainment inventory should represent emissions during the same 5-year period associated with the air quality data used to determine that the area meets the applicability requirements of the LMP option. The Columbia Falls, Kalispell and Libby LMPs include an emission inventory from 2014, representative of the 2013-2017 5-year period which served as the 5-year period relied upon in the LMPs as meeting the air quality data requirements of the LMP option memo.
The 1990 CAA Amendments contained revisions to the NSR program requirements for the construction and operation of new and modified major stationary sources located in NAA. The CAA requires states to amend their SIPs to reflect these revisions, but does not require submittal of this element along with the other SIP elements. The CAA established June 30, 1992, as the submittal date for the revised NSR programs (section 189 of the CAA).
Montana has a fully approved nonattainment NSR program, most recently approved on August 30, 1995 (60 FR 45051). Montana also has a fully approved PSD program, most recently approved on August 30, 1995 (60 FR 45051). Upon the effective date of redesignation of an area from nonattainment to attainment, the requirements of the Part D NSR program will be replaced by the PSD program and the maintenance area NSR program.
Once an area is redesignated, the state must continue to operate an appropriate air monitoring network in accordance with 40 CFR part 58 to verify attainment status of the area. The State of Montana operates one PM10 SLAMS in each of the NAAs. The Flathead Valley, Kalispell and Libby monitoring sites meet EPA SLAMS network design and siting requirements set forth at 40 CFR part 58, appendices D and E. In section 3.4 of each of the LMPs that we are proposing to approve, the State commits to continued operation of the monitoring network.
The CAA requires that contingency measures take effect if the area fails to meet RFP requirements or fails to attain the NAAQS by the applicable attainment date. Since the Columbia Falls, Kalispell and Libby NAAs have attained the 1987 24-hour PM10 NAAQS, contingency measures are no longer required under section 172(c)(9) of the CAA. However, contingency provisions are required for maintenance plans under section 175(a)(d). We describe the contingency provisions Montana provided in the LMP section below.
Part D subpart 4, section 189(a), (c) and (e) requirements apply to any Moderate NAA area before the area can be redesignated to attainment. The requirements which were applicable prior to the submission of the request to redesignate the area must be fully approved into the SIP before redesignating the area to attainment. These requirements include: (a) Provisions to assure that RACM was implemented by December 10, 1993; (b) Either a demonstration that the plan provided for attainment as expeditiously as practicable but not later than December 31, 1994, or a demonstration that attainment by that date was impracticable; (c) Quantitative milestones which were achieved every 3 years and which demonstrate RFP toward attainment by December 31, 1994; and (d) Provisions to assure that the control requirements applicable to major stationary sources of PM10 also apply to major stationary sources of PM10 precursors except where the Administrator determined that such sources do not contribute significantly to PM10 levels which exceed the NAAQS in the area. These provisions were fully approved into the SIP upon the EPA's approval of the PM10 Moderate area plan for the Columbia Falls, Kalispell and Libby NAAs on March 19, 1996, March 19, 1996, and August 30, 1994, respectively.
The state must be able to reasonably attribute the improvement in air quality to permanent and enforceable emission reductions. In making this showing, the state must demonstrate that air quality improvements are the result of actual enforceable emission reductions. This showing should consider emission rates, production capacities, and other related information. The analysis should assume that sources are operating at permitted levels (or historic peak levels) unless evidence is presented that such an assumption is unrealistic. Permanent and enforceable control measures in the Columbia Falls, Kalispell and Libby NAA SIPs include RACM. Emission sources in the three NAAs have been implementing RACM for at least 10 years.
Areas that qualify for the LMP will meet the NAAQS, even under worst case meteorological conditions. Under the LMP option, the maintenance demonstration is presumed to be satisfied if an area meets the qualifying criteria. Thus, by qualifying for the LMP, Montana has demonstrated that the air quality improvements in the Columbia Falls, Kalispell and Libby NAAs are the result of permanent emission reductions and not a result of either economic trends or meteorology. A description of the LMP qualifying criteria and how the Columbia Falls, Kalispell and Libby areas meet these criteria is provided in the following section.
Emissions in the Columbia Falls NAA have been reduced 87.8% since 1990. The primary controls incorporated into the SIP were rules specifying the allowed material to be placed on roads and parking lots for sanding and chip Start Printed Page 16034sealing; rules specifying street sweeping and flushing requirements during the winter and summer months to reduce fugitive road dust; rules requiring the paving of new roads within the Columbia Falls Control District; and permit requirements on the Plum Creek sawmill, plywood and MDF facilities in Columbia Falls. Fugitive road dust comprised nearly 51% of the uncontrolled emissions when the area was designated nonattainment, and emissions from the Plum Creek facility accounted for 44% of the area's uncontrolled emissions. Based on the 2014 NEI, current fugitive road dust emissions are less than 8% of their 1990 levels and current emissions from the Plum Creek facility are 14% of their uncontrolled emissions.
Emissions in the Kalispell NAA have been reduced 74.0% since 1998. The primary controls incorporated into the SIP were rules specifying the allowed material to be placed on roads and parking lots for sanding and chip sealing; rules specifying street sweeping and flushing requirements during the winter and summer months to reduce fugitive road dust; rules requiring the paving of new roads within the Kalispell Control District; and permit requirements on 11 stationary sources in the NAA.
Emissions in the Libby NAA have been reduced 90.2% since 1989. The primary controls incorporated into the SIP were air pollution control rules in Chapter 1, Subchapters 1 through 4, addressing solid fuel burning devices, reentrained road dust control, and outdoor burning regulations. Additionally, the control plan accounted for industrial emission reductions through permit revisions. These revisions required that RACT be applied to the Champion International boilers which resulted in derating Boiler #7, reducing allowable emissions from Boiler #8, and adding new controls on Boiler #9. Changing economic conditions, ultimately saw the closure of the wood products facility after a previous sale of the facility to Stimson Lumber Company. The source specific limits on the Champion International boilers remain in the SIP.
In this action, we are proposing to approve the LMPs for the Columbia Falls, Kalispell and Libby NAAs in accordance with the principles outlined in the LMP Option.
The LMP Option memo outlines the requirements for an area to qualify for the LMP Option. First, the area should be attaining the NAAQS. As stated above in Section III.A., the EPA has determined that the Columbia Falls, Kalispell and Libby NAAs are attaining the PM10 NAAQS.
Second, the average design value (ADV) for the past 5 years of monitoring data (2014-2018) must be at or below the CDV. As noted in Section II.B., the CDV is a margin of safety value and is the value at which an area has been determined to have a 1 in 10 probability of exceeding the NAAQS. The LMP Option memo provides two methods for review of monitoring data for the purpose of qualifying for the LMP option. The first method is a comparison of a site's ADV with the CDV of 98 µg/m3 for the 24-hour PM10 NAAQS. A second method that applies to the 24-hour PM10 NAAQS is the calculation of a site-specific CDV and a comparison of the site-specific CDV with the ADV for the past 5 years of monitoring data. Tables 3, 4 and 5 outline the design values for the years 2014-2018, and present the ADV.
Tables 6, 7 and 8 summarize the wildfire related events that were excluded from the calculated design values in Tables 3, 4 and 5, respectively. Tables 6, 7 and 8 include all regionally concurred exceptional events, as well as values between 98 µg/m[3] and 155 µg/m[3] , which were treated in a manner analogous to exceedance data under the Exceptional Events Rule (EER) for the purpose of determining the LMP option eligibility.[3] The values between 98 µg/m[3] and 155 µg/m[3] will remain in the Air Quality System (AQS) database for use in calculating DV's for every purpose besides determining LMP eligibility.[3] The EER can be found in 40 CFR 50.14 and 40 CFR 51.930, and outlines the requirements for the treatment of monitored air quality data that has been heavily influenced by an exceptional event. 40 CFR 50.1(j) defines an exceptional event as an event which affects air quality, is not reasonably controllable or preventable, is an event caused by human activity that is unlikely to recur at a particular location or a natural event and is determined by the Administrator in accordance with 40 CFR 50.14 to be an exceptional event. Exceptional events do not include stagnation of air masses or meteorological inversions, meteorological events involving high temperatures or lack of precipitation, or air pollution relating to source noncompliance. 40 CFR 50.14(b) states that the EPA shall exclude data from use in determinations of exceedances and NAAQS violations where a state demonstrates to the EPA's satisfaction that an exceptional event caused a specific air pollution concentration in excess of one or more NAAQS at a particular air quality monitoring location and otherwise satisfies the requirements of section 50.14. Tables 6, 7 and 8 below include some exceptional events not formally concurred on by EPA. These exceptional events were excluded by EPA in accordance with the LMP guidance (see footnote 3). We have concurred that these values can be excluded for the sole purpose of determining PM10 Limited Maintenance Plan (LMP) eligibility and supporting documentation of EPA's concurrence with the wildfire related events can be found in the docket.[4]
Table 3—Summary of 24-Hour PM10 Design Values (µg/m3) for Columbia Falls 2014-2018
Based on data from Flathead Valley (Soccer Complex.) Site, AQS Identification Number (30-029-0049)
Design value years
Design concentration (µg/m3)
2014-2016 60 Flathead Valley Soccer Complex.
2015-2017 66 Flathead Valley Soccer Complex.
2016-2018 74 Flathead Valley Soccer Complex.
Average Design Concentration (Of Most Recent 3 Design Concentrations) 67
Table 4—Summary of 24-Hour PM10 Design Values (µg/m3) for Kalispell 2014-2018
Based on data from Flathead Electric. Site, AQS Identification Number (30-029-0047)
2014-2016 89 Flathead Electric.
2015-2017 88 Flathead Electric.
2016-2018 90 Flathead Electric.
Average Design Concentration (Of Most Recent 3 Design Concentrations) 89
Table 5—Summary of 24-Hour PM10 Design Values (µg/m3) for Libby 2014-2018
Based on data from Libby Courthouse Annex. Site, AQS Identification Number (30-053-0018)
2014-20161 90 Courthouse Annex.
2015-20171 92 Courthouse Annex.
2016-2018 95 Courthouse Annex.
Average Design Concentration (Of Most Recent 3 Design Concentrations) 92
Table 6—24-Hour PM10 Events Excluded from 2014-2018 Columbia Falls Design Values
24-Hour Value (µg/m3)
8/20/2015 140 Flathead Valley Soccer Complex.
8/21/2015 112 Flathead Valley Soccer Complex.
8/23/2015 112 Flathead Valley Soccer Complex.
8/24/2015 139 Flathead Valley Soccer Complex.
8/25/2015 109 Flathead Valley Soccer Complex.
8/26/2015 112 Flathead Valley Soccer Complex.
8/27/2015 136 Flathead Valley Soccer Complex.
8/28/2017 135 Flathead Valley Soccer Complex.
8/29/2015 138 Flathead Valley Soccer Complex.
9/6/2017 * 182 Flathead Valley Soccer Complex.
9/7/2017 * 228 Flathead Valley Soccer Complex.
9/8/2017 * 225 Flathead Valley Soccer Complex.
9/9/2017 126 Flathead Valley Soccer Complex.
9/13/2017 102 Flathead Valley Soccer Complex.
* EPA-Concurred Exceptional Event [other exceptional events not formally concurred on by EPA, were excluded by EPA in accordance with the LMP guidance, see footnote 3].
Table 7—24-Hour PM10 Events Excluded from 2014-2018 Kalispell Design Values
8/20/2015 125 Flathead Electric.
8/21/2015 103 Flathead Electric.
8/24/2015 139 Flathead Electric.
8/26/2015 125 Flathead Electric.
8/27/2015 123 Flathead Electric.
Start Printed Page 16036
8/28/2017 133 Flathead Electric.
8/29/2015 146 Flathead Electric.
9/5/2017 131 Flathead Electric.
9/6/2017 * 171 Flathead Electric.
9/7/2017 * 194 Flathead Electric.
9/8/2017 * 228 Flathead Electric.
9/9/2017 154 Flathead Electric.
9/13/2017 * 158 Flathead Electric.
* EPA-Concurred Exceptional Event [other events not formally concurred on by EPA, were excluded by EPA in accordance with the LMP guidance, see footnote 3].
Table 8—24-Hour PM10 Events Excluded from 2014-2018 Libby Design Values
8/20/2015 113 Courthouse Annex.
8/24/2015 * 180 Courthouse Annex.
8/25/2015 102 Courthouse Annex.
8/27/2015 109 Courthouse Annex.
8/29/2015 143 Courthouse Annex.
9/5/2017 104 Courthouse Annex.
9/6/2017 101 Courthouse Annex.
9/7/2017 134 Courthouse Annex.
9/8/2017 * 158 Courthouse Annex.
The ADV for the 24-Hour PM10 NAAQS for Columbia Falls, Kalispell and Libby, based on data from the SLAMS monitors for the years 2014-2018, are 67 µg/m3, 89 µg/m3, and 92 µg/m3, respectively. These values fall below the presumptive 24-Hour CDV of 98 µg/m3, and would all meet the first threshold for LMP eligibility. However, in the case of both Kalispell and Libby, these areas required the calculation of an area specific CDV in order to pass the motor vehicle regional emissions analysis test, described below and in further detail in the LMP guidance document.[5] Table 9 lists the respective CDV for each of the NAAs based on data from 2014-2018, utilized for satisfying all the LMP requirements. Calculation of the 2014-2018 CDV for Kalispell and Libby can be found in the supporting documents in the docket.[6]
Table 9—Critical Design Values Used for Determining LMP Eligibility
PM10 NAA
24-Hour CDV (µg/m 3)
2013-2018 ADV (µg/m 3)
Columbia Falls * 98 97
Kalispell 124 89
Libby 139.9 92
* Use of presumptive CDV as described in the LMP guidance document.
In addition to having an ADV that is lower than either the presumptive or area specific CDV, in order to qualify for the LMP, the area must meet the motor vehicle regional emissions analysis test in attachment B of the LMP Option memo. Using the methodology outlined in the memo, based on monitoring data for the period 2016-2018, the EPA has determined that the Columbia Falls, Kalispell and Libby NAAs all pass the motor vehicle regional emissions analysis test, with a projected DV of 74.3 µg/m[3] , 109.7 µg/m[3] and 100.3 µg/m[3] after 10 years, respectively, attributable to motor vehicle emission growth. For the calculations used to determine how the Columbia Falls, Kalsipell and Libby NAAs passed the motor vehicle regional analysis test, see the supporting documents in the docket.[7]
The monitoring data for the period 2016-2018 shows that Columbia Falls, Kalispell and Libby have attained the 24-hour NAAQS for PM10, and the 24-hour ADV for each of the areas is less than the 24-hour PM10 presumptive and area-specific CDV. Finally, the areas have met the regional vehicle emissions analysis test. Thus, the Columbia Falls, Kalispell and Libby NAAs qualify for the LMP Option described in the LMP Option memo. The LMP Option memo also indicates that once a state selects the LMP Option and it is in effect, the state will be expected to determine, on an annual basis, that the LMP criteria are still being met. If the state Start Printed Page 16037determines that the LMP criteria are not being met, it should take action to reduce PM10 concentrations enough to requalify for the LMP. One possible approach the state could take is to implement contingency measures. Please see section 3.6 of each of the three LMPs for a description of contingency provisions submitted as part of the State's submittal.
The state's approved attainment plan should include an emissions inventory (attainment inventory) which can be used to demonstrate attainment of the NAAQS. The inventory should represent emissions during the same 5-year period associated with air quality data used to determine whether the area meets the applicability requirements of the LMP Option. The state should review its inventory every 3 years to ensure emissions growth is incorporated in the attainment inventory if necessary. In this instance, Montana completed an attainment year inventory for the attainment year 2014 for all three NAAs. The EPA has reviewed the 2014 emissions inventories and determined that they are current, accurate and complete. In addition, the emissions inventory submitted with the LMP for the calendar year 2014 is representative of the level of emissions during the time period used to calculate the ADV since 2014 is included in the 5-year period used to calculate the design values (2013-2017).
PM10 monitoring networks for the Columbia Falls, Kalispell and Libby NAAs have been developed and maintained in accordance with federal siting and design criteria in 40 CFR part 58, appendices D and E and in consultation with the EPA Region 8. In Section 3.4 of the Columbia Falls, Kalispell and Libby LMPs, Montana states that it will continue to operate its monitoring network to meet EPA requirements.
Section 175A of the CAA states that a maintenance plan must include contingency provisions, as necessary, to promptly correct any violation of the NAAQS which may occur after redesignation of the area to attainment. As explained in the LMP Option memo, these contingency measures do not have to be fully adopted at the time of redesignation. As noted above, CAA section 175A requirements are distinct from CAA section 172(c)(9) contingency measures. Section 3.6 of the Columbia Falls, Kalispell and Libby LMPs describe a process and timeline to identify and evaluate appropriate contingency measures in the event of a quality assured violation of the PM10 NAAQS. Upon notification of a PM10 exceedance in any of the three areas, the MDEQ and the appropriate local government will develop contingency measures designed to prevent or correct a violation of the PM10 standard. This process will be completed within twelve months of the exceedance notification. Upon violating the PM10 standard, the MDEQ and local government will determine if the local contingency measures will be adequate to prevent further exceedances or violations. If the agencies determine that local measures will be inadequate, the MDEQ and local government will adopt state-enforceable measures.
The current and proposed contingency provisions in the Columbia Falls, Kalispell and Libby LMPs meet the requirements for contingency provisions as outlined in the LMP Option memo.
Transportation conformity is required by section 176(c) of the CAA. Conformity to a SIP means that transportation activities will not produce new air quality violations, worsen existing violations, or delay timely attainment of the NAAQS (CAA section 176(c)(1)(B)). The EPA's conformity rule at 40 CFR part 93, subpart A requires that transportation plans, programs and projects conform to SIPs and establishes the criteria and procedures for determining whether or not they conform. To effectuate its purpose, the conformity rule typically requires a demonstration that emissions from the applicable Regional Transportation Plan and the Transportation Improvement Program are consistent with the motor vehicle emission budget (MVEB) contained in the control strategy SIP revision or maintenance plan (40 CFR 93.101, 93.118, and 93.124). The EPA notes that a MVEB is usually defined as the level of mobile source emissions of a pollutant relied upon in the attainment or maintenance demonstration to attain or maintain compliance with the NAAQS in the nonattainment or maintenance areas. MVEBs are, however, treated differently with respect to LMP areas.[8]
Our LMP Option memorandum does not require that MVEBs be identified in the maintenance plan. While the EPA's LMP Option memorandum does not exempt an area from the need to affirm conformity, it explains that the area may demonstrate transportation conformity without identifying and submitting a MVEB. The basis for this provision is that it is unreasonable to expect that an LMP area will experience so much growth during the maintenance period that a violation of the PM10 NAAQS would result. Therefore, for transportation conformity purposes, the EPA has concluded that mobile source emissions in LMP areas need not be capped, with respect to a MVEB, for the maintenance period and a regional emissions analysis (40 CFR 93.118), for transportation conformity purposes, is also not required.
However, since LMP areas are still maintenance areas, certain aspects will continue to be required for transportation projects located within the Columbia Falls, Kalispell and Libby PM10 maintenance areas. Specifically, for conformity determinations, projects will have to demonstrate that they are fiscally constrained (40 CFR 93.108) and meet the criteria for consultation (40 CFR 93.105 and 40 CFR 93.112) and timely implementation (as applicable) of Transportation Control Measures (40 CFR 93.113). In addition, projects located within the Columbia Falls, Kalispell and Libby PM10 LMP areas will be required to be evaluated for potential PM10 hot-spot issues in order to satisfy the “project level” conformity determination requirements. As appropriate, a project may then need to address the applicable criteria for a PM10 hot-spot analysis as provided in 40 CFR 93.116 and 40 CFR 93.123.
Finally, our proposed approval of the Columbia Falls, Kalispell and Libby PM10 LMPs affect future PM10 project-level transportation conformity determinations as prepared by the Montana Department of Transportation in conjunction with the Federal Highway Administration and the Federal Transit Administration. See 40 CFR 93.100. As such, the EPA is proposing to approve the Columbia Falls, Kalispell and Libby LMPs as meeting the appropriate transportation Start Printed Page 16038conformity requirements found in 40 CFR part 93, subpart A.
Federal actions, other than transportation conformity, that meet specific criteria need to be evaluated with respect to the requirements of 40 CFR part 93, subpart B. The EPA's general conformity rule requirements are designed to ensure that emissions from a federal action will not cause or contribute to new violations of the NAAQS, exacerbate current violations, or delay timely attainment. However, as noted in our LMP Option memorandum and similar to the above discussed transportation conformity provisions, federal actions subject to our general conformity requirements would be considered to satisfy the “budget test,” as specified in 40 CFR 93.158(a)(5)(i)(A). As discussed above, the basis for this provision in the LMP Option memorandum is that it is unreasonable to expect that an LMP area will experience so much growth during the maintenance period that a violation of the PM10 NAAQS would result. Therefore, for purposes of general conformity, a general conformity PM10 emissions budget does not need to be identified in the maintenance plan, nor submitted, and the emissions from federal agency actions are essentially considered to not be limited.
For the reasons explained in Section III, we are proposing to approve the LMP for the Columbia Falls, Kalispell and Libby NAAs and the State's request to redesignate the Columbia Falls, Kalispell and Libby NAAs from nonattainment to attainment for the 1987 24-hour PM10 NAAQS. Additionally, the EPA is proposing to determine that the Kalispell and Libby NAAs have attained the NAAQS for PM10. This determination is based upon monitored air quality data for the PM10 NAAQS during the years 2016-2018. The EPA is proposing to approve the Columbia Falls, Kalispell and Libby LMPs as meeting the appropriate transportation conformity requirements found in 40 CFR part 93, subpart A.
1. The “Procedures for Processing Requests to Redesignate Areas to Attainment” (Calcagni memo) outlines the criteria for redesignation. The Calcagni memo can be found at https://www.epa.gov/​sites/​production/​files/​2016-03/​documents/​calcagni_​memo_​-_​procedures_​for_​processing_​requests_​to_​redesignate_​areas_​to_​attainment_​090492.pdf.
2. The “Limited Maintenance Plan Option for Moderate PM10 Nonattainment Areas” outlines the criteria for development of a PM10 limited maintenance plan and can be found at https://www.epa.gov/​sites/​production/​files/​2016-06/​documents/​2001lmp-pm10.pdf.
3. Update on Application of the Exceptional Events Rule to the PM10 Limited Maintenance Plan Option, US EPA, William T. Harnett, Director, Air Quality Policy Division, OAQPS, May 7, 2009.
4. February 8, 2019 letter to MDEQ, Re: Exceptional Events Requests Regarding Exceedances of the 24-hour PM10 NAAQS and the LMP Eligibility Threshold at Montana Monitoring Sites with PM10 Nonattainment Areas; and November 1, 2018 letter to MDEQ, Re: Request for EPA concurrence on exceptional event claims for fine (PM2.5) and coarse (PM10) particulate matter data impacted by wildfires in 2015 and 2016.
5. “Limited Maintenace Plan Option for Moderate PM10 Nonattainment Areas—Attachment B.”
6. Memo to file “Critical Design Value Calculations for the Kalispell and Libby PM10 NAAs.”
7. See memo to file dated October 24, 2018 titled “Columbia Falls, Kalispell and Libby Motor Vehicle Regional Emissions Analysis.”
8. Further information concerning the EPA's interpretations regarding MVEBs can be found in the preamble to the EPA's November 24, 1993, transportation conformity rule (see 58 FR 62193-62196).
[FR Doc. 2020-05671 Filed 3-19-20; 8:45 am]