New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 1 CHAPTER 10: BEST AVAILABLE RETROFIT TECHNOLOGY (BART) EVALUATION

10.1 Introduction

In 1999, the EPA published a final rule to address a type of visibility impairment known as regional haze

. See 64 F ed. R eg. 35714 , July 1, 1999. The regional haze rule requires States to submit state implementation plans (SIPs) to address regional haze visibility impairment in 156 Federally

- protected parks and wilderness areas. The 1999 rule was issued to fulfill a long

- standing EPA commitment to address regional haze under the authority and requirements of sections 169A and 169B of the Clean Air Act (CAA). 1

As required by the CAA, the EPA included in the final regional haze rule a requirement for Bes t Available Retrofit Technology (BART) for certain large stationary sources. The regulatory requirements

for BART were codified at 40 CFR § 5 1 .308(e) and in definitions that appear in 40 CFR § 5 1 .301.

The BART

- eligible sources are those sources which ha ve the potential to emit 250 tons per year or more of a visibility impairing air pollutant, were put in place between August 7, 1962 and August 7, 1977, and whose operations fall within one or more of 26 specifically listed source categories. Under the CA A, BART is required for any BART

- eligible source which a State determines “emits any air pollutant which may reasonably be anticipated to cause or contribute to any impairment of visibility in any such area.” Accordingly, for stationary sources meeting th ese criteria, States must address the BART requirement when they develop their regional haze SIPs.

The EPA published a second rulemaking on June 6, 2005 that made changes to the Final Rule published July 1, 1999. The second rulemaking was in response to a U.S. Court of Appeals for the D.C. Circuit ruling that vacated part of the regional haze rule

, American Corn Growers v. EPA, 291 F.3d 1 (D.C. Cir.
2002)



### . The June 6, 2005 Final Rule required the BART analysis to include an analysis of the degree of

visi bility improvement resulting from the use of control technology at BART

- subject sources; included new BART Guidelines contained in a new Appendix Y to Part 51; and added the requirement that States use Appendix Y for determining BART at certain large elect rical generating units (EGUs).

The Guidelines also contained specific presumptive limits for SO 2 and NOx for certain large EGUs based on fuel type, unit size, cost effectiveness, and presence or absence of pre

- existing controls. The

Guidelines directs states to generally require owners and operators to meet the presumptive limits at coal

fired EGUs greater than 200 MW at power plants with a total generating capacity greater than 750 MW

, unless the state determine s that an alternative control le vel is justified based on consideration of the statutory factors

. The presumptive limits for NOx are based on coal type, boiler type and whether post

combustion controls are already installed at the source.

As originally adopted by the Board on June 3, 2 011, this Chapter 10 of New Mexico’s § 309(g) SIP contained the Department’s determinations of BART for the San Juan Generating Station (“San Juan”) with respect to sulfur dioxide (“SO 2 ”), particulate matter (“PM”), and nitrogen oxides (“NOx”). In

Novembe r 2012, the EPA promulgated final approval of these BART determinations with respect to SO 2 and PM, but took no action on New Mexico’s NOx BART determination for San Juan. 77 Fed. Reg.
36,044 (Nov. 27, 2012). EPA had previously issued a federal implementa tion plan (“FIP”) containing a

different NOx BART determination for San Juan. 76 Fed. Reg. 52,388 (Aug. 22, 2011).

In an attempt t o resolve litigation arising from New Mexico’s and EPA’s incompatible San Juan NOx

BART determination s , New Mexico, the U.S . EPA, and PNM reached a tentative agreement on an alternative plan to address pollution control requirements for the San Juan Generating Station under theNew Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 2 Clean Air Act’s requirements for regional haze and interstate transport for visibility. See Appendix G, Term Sheet Between the U.S. Environmental Protection Agency, Public Service Company of New Mexico and the State of New Mexico (“Term Sheet”) . This plan, referred to hereinafter as the “State

Alternative

, ” calls for the complete shutdown of Units 2 and 3 by the end of 2017, and the installation of

selective non

- catalytic reduction (“SNCR”) on Units 1 and 4.

Under the process and schedule provided in the Term Sheet, NMED agreed to seek approval by the Environmental Improvement Board (“Board”) of a SIP revision containing the substantive provisions of the Term Sheet, including a five

- factor analysis of the State Alternative as a NOx BART determination. This revised Chapter 10 and the BART analysis in revised Appendix D fulfill that requirement of the Term Sheet. If approved by the Board, this SIP revision will be submitted to EPA for approval, disapproval, or partial approval, in accordance with applicable notice

- and

- comment rulemaking requirements. As stipulated in the Term Sheet, “NMED and EPA intend that the Regional Haze and Interstate Transport 1 SIP revisions as adopted and submitted to EPA will, if approved by EPA, lead to EPA action withdrawing the federal implementation plan for [San Juan].”

In light of this agreement to submit a revis ed SIP and in accordance with the Term Sheet schedule , on February 22, 2013 NMED request ed that EPA hold in abeyance its consideration of the portion of New Mexico’s 2011 Regional Haze SIP addressing a NOx BART determination for San Juan.

In order to ma intain New Mexico’s BART analyses together in one location within the SIP in addition to meeting the Term Sheet requirements , this revised Chapter 10 continues to contain a description of the statewide BART determination process, reviews the 2011 BART dete rminations for San Juan, and
[ adopts ] evaluates the State Alternative [ as New Mexico’s NOx BART determination for San Juan. ]

, including voluntary unit retirements as a new alternative operating scenario that had not previously been analyzed.

In summary, t his revised Chapter 10 of the New Mexico SIP adopts the State Alternative as New

Mexico’s NOx BART determination for San Juan and, if approved by EPA, will supersede the San Juan NOx BART determination contained in the 2011 Regional Haze SIP

.

10. 2 SO 2 : Regional SO 2 Milestone and Backstop Trading Program

New Mexico is a “ § 309 ” (40 CFR § 51.309) state participating in the Regional SO 2 Milestone and Backstop Trading Program. Section 308(e)(2) provides states with the option to implement or require

p articipation in an emissions trading program or other alternative measure rather than to require sources subject to BART to install, operate, and maintain additional control technology to meet an established emission limit on a continuous basis. However, t he alternate program must achieve greater reasonable progress than would be accomplished by installing BART at each source subject to BART . A demonstration that the alternate program can achieve greater reasonable progress is prescribed by §308(e)(2)(i). Section 309(d)(4)(i) requires that the SO 2 milestones established under the Plan “...must be shown to provide for greater reasonable progress than would be achieved by application of BART pursuant to §51.308(e)(2).”

New Mexico participated in creat ing a de tailed report entitled “ Demonstration that the SO 2 Milestones Provide Greater Reasonable Progress than BART ” covering SO 2 emissions from all states participating in the Regional SO 2 Milestone and Backstop Trading Program. The document is included in New Me xico's §309 Regional Haze SIP submittal to EPA.

1 NMED is requesting approval of the related Interstate Transport SIP revision in a separate hearing before the

Board.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 3 As part of the §309 program, participating states, including New Mexico, must submit an annual Regional Sulfur Dioxide Emissions and Milestone Report that compares actual emissions to pre

- established milestones. Participating states have been filing these reports since 2003. Each year, states have been able

to demonstrate that actual SO2 emissions are well below the milestones. The actual emissions and their respective milestones are shown in Table 10

- 1 below:

Table 1 0

- 1 : Regional Sulfur Dioxide Emissions and Milestone Report Summary

Year Reported SO 2 Emissions (tons) 3

- year Milestone Average (tons)

2003 330,679 447,383

2004 337,970 448,259

2005 304,591 446,903

2006 279,134 420,194

2007 273,663 420,637

2008 244,189 378,398

On November 27, 2012, the EPA approved New Mexico’s SO 2 backstop trading program under 40 CFR § § 51.309 and 51.308(e)(2) as achieving greater reasonable progress than BART. 77 Fed. Reg. 36,044

. Notwithstanding the fact that t he BART requirement has thus been satisfied statewide with respect to

SO 2 , additional SO 2 reductions will be made at the San Juan Generating Station under the “State

Alternative” described below.

10.3 Determination of Sources Subject to BART

Under the BART Guidelines, a state is required to take the following steps in its BART analysis: (a)

i dentify all “BART eligible” sources, (b) identify sources “subject to BART,” (c) determine what BART is for each source subject to BART, and (d) establish emission limits consistent with the BART determination for each source subject to BART. See 70 Fed. Reg. at 39,158. In New Mexico, the result of steps (a) and (b) was the determination that only one source is subject to BART, the San Juan Generating Station, as discussed below. Steps (c) and (d) as applied to San Juan are discussed in section

10.4 bel ow.

10.3.1 BART Eligible Sources

Under the CAA and the BART Guidelines, s tates are required to identify each source that satisf ies all of the following criteria: it fall s within the 26 listed source categories as listed in the CAA, it was “in

existence” on August 7, 1977 but w as not “in operation” before August 7, 1962, and it has a current potential to emit that is greater than 250 tons per year of any single visibility impairing pollutant.

In May 2006, the Department conducted a review of sources poten tially subject to the BART rule. New

Mexico identified 11 sources as BART

- eligible sources as part of this review. The 11 BART eligible sources identified in New Mexico are Giant Refining, Ciniza Refinery (now Western Refining Southwest, Gallup Refinery); Public Service Company of New Mexico, San Juan Generating Station Boilers 1 through 4; Giant Refining San Juan Refinery (now Western Refining Southwest, Bloomfield Refinery) Unit #1 fluid catalytic cracking unit electrostatic precipitator; DEFS Artesia Gas Plant (now DCP Midstream Artesia Gas Plant) sulfur recovery unit; Amoco Empire Abo (now Frontier Field Services Empire Abo Gas Plant) sulfur recovery unit; Marathon Indian Basin Gas Plant (now Oxy USA WTP Indian Basin Gas Plant) sulfur recovery unit; DEFS Linam Ranch Gas Plant (now DCP Midstream Linam Ranch Gas Plant) sulfur recovery unit, Dynegy Saunders (now Versado Gas Processors Saunders Gas Plant) sulfur recovery unit; Southwestern Public Service Cunningham Station; Southwestern Public

Service Maddox Station; El Paso Rio Grande Generating Station.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 4 10.3.2 Sources Subject to BART

After determining BART

- eligibility, the State must then determine whether the source is [ potentially ] subject

- to

- BART. EPA finalized several options that allowed States flexibility when making the

det ermination of whether a source “ emits any pollutants which may reasonably be anticipated to cause or contribute to any visibility impairment. ”

Option 1: All BART

- eligible sources are Subject to BART

EPA provided the States with the discretion to consider all BART

- eligible sources within the State to be

“ reasonably anticipated to cause or contribute ” to some degree of visibility impairment in a Class I area. EPA held that this option is consistent with the American Corn Growe rs court's decision, as it would be an impermissible constraint of State authority for the EPA to force States to conduct individualized analyses in order to determi ne that a BART

- eligible source “ emits any air pollutant which may reasonably anticipated to cause or contribute to any impairment of vi sibility in any [Class I] area.”

Option 2: All BART

- Eligible Sources Do Not Cause or Contribute to Regional Haze

EPA also provided States with the option of performing an analysis to show that the full group of BART

eligible sources in a State may not, as a whole, be reasonably anticipated to cause or contribute to any visibility impairment in Class I areas. Although the option was provided, EPA did also state that it anticipated that in most, if not all States, BART eligible

- sources are likely to cause or contribute to some level of visibility impairment in at least one Class I area.

Option 3: Case

- by

- Case BART Analysis

The final option provided to the States was to consider the individual contributions of a B ART

- eligible source to determine whether the facility is subject

- to

- BART. Specifically, EPA allowed States to choose to undertake an analysis of each BART

- eligible source in the State in consid ering whether each such

source “ emit[s] any air pollutant which may reasonably be anticipated to cause or contribute to any impairment of vi sibility in any [Class I] area.” The Guidelines provide that a source with a visibility impact of 1.0 dv should be considered to cause visibility impairment, and a source with a v isibility impact

of 0.5 dv should be considered to contribute to visibility impairment. Alternatively, States may choose to presume that all BART

- eligible sources within the State meet this applicability test, but provide sources with the ability to demon strate on a case

- by

- case basis that this is not the case.

The Department determined that the third option is the most consistent with the American Corn Growers case, as this option provides a rebuttable method for the evaluation of the visibility impact f rom a single source. If the air dispersion modeling analysis shows that a facility causes or contributes to Regional Haze, then it is required to address BART. A State is also provided with flexibility under this option, as it may exempt from BART any sour ce that is not reasonably anticipated to cause or contribute to visibility degradation in a Class I area.

The Western Regional Air Partnership (WRAP) performed the initial BART modeling for the state of New Mexico. The procedures used are outlined in the WRAP Regional Modeling Center (RMC) BART Modeling Protocol that is available at:

http://pah.cert.ucr.edu/aqm/308/bart/WRAP_RMC_BART_Protocol_Aug15_2006.pdf

The basic assumptions in the WRAP BART CALMET/CALPUFF modeling used for New Mexico are as

follows:New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 5 • Use of three years of modeling of 2001, 2002, and 2003.

• Visibility impacts due to emissions of SO 2 , NOx and primary PM emissions were calculated. PM

emissi ons were modeled as PM 2.5

.

• Visibility was calculated using the Original IMPROVE equation and Annual Average Natural

Conditions.

Initial modeling was performed for the 11 source complexes in New Mexico with visibility estimated

from the sources’ SO 2 , NOx , and PM emissions. Then for those sources whose 98 th percentile visibility impacts at any Class I area due to their combined SO 2 , NOx, and PM emissions exceeded the 0.5 dv significance threshold, the separate contribution to visibility at Class I areas wa s assessed for SO 2 alone (SO 4 ), NOx alone (NO 3 ), PM alone (PMF) and combined NOx plus PM emissions (NO 3 + PMF).

Of the 11 source complexes analyzed, only one source complex’s visibility impacts at any Class I area

due to combined SO 2 , NOx, and PM emissions exceeded the 0.5 dv threshold (PNM San Juan Generating

Station Boilers #1

- 4). Of the 10 other source complexes, none exceed a 0.33 dv impact. See Appendix C. Consequently, only the PNM San Juan Boilers #1

- 4 were subjected to a BART determination. 2

On November 9, 2006, the New Mexico Environment Department informed PNM that the modeling performed by the WRAP indicated the visibility impairment from the San Juan Generating Station (SJGS) was over the 0.5 dv threshold, and was therefore subject to a BART determination. The results are presented in Table 10

- 2 below. In response, Black & Veatch (B&V), on behalf of PNM, submitted the BART Modeling Protocol document which described the CALPUFF modeling methodology to be used as part of the BART engineeri ng evaluation for Units 1

- 4 at the SJGS. [ The results are presented in Table

10

- 2 below. ]

2 On November 27, 2012, EPA approved al l elements of New Mexico’s 2011 regional haze SIP except for the NOx BART determination for San Juan, thereby approving New Mexico’s determination of which sources are subject

- to

BART. 77 FR 70,693.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 6 Table 1 0

- 2 : Visibility Impact Analysis of PNM's San Juan Generating Station NM SRC02 Unit # 350450902, PNM SJ #1

- 4: SO 2 = 35,735 TPY; NOx = 38,763 TPY; PM = 3,884 TPY Annual Average Natural Conditions Class I Area with at least 1 receptor within 300 km of source

Class I Area Minimum

Distance 98th Percentile for Each Year 98th

(km) 2001 2002 2003 3 year

AVG

Mesa Verde NP 40 5.54 5.34 5.30 5.40

Weminuche Wilderness 98 2.24 2.99 2.41 2.55

San Pedro Parks Wilderness 155 3.80 4.07 4.14 4.01

La Garita Wilderness 169 1.63 1.82 1.77 1.74 Canyonlands NP 170 6.21 4.33 4.44 4.99 Black Canyon Gunnison NM 203 2.38 2.27 2.43 2.36

Bandelier NM 210 2.47 2.90 3.08 2.82

Petrified Forest NP 213 1.62 1.27 1.03 1.31

West Elk Wilderness 216 2.14 1.90 2.20 2.08

Arches NP 222 4.06 3.71 3.59 3.79 Capitol Reef NP 232 4.00 2.02 2.35 2.79

Pecos Wilderness 248 2.17 2.63 2.81 2.53

Wheeler Peak Wilderness 258 1.94 1.73 1.97 1.88

Great Sand Dunes NM 269 1.47 1.59 1.74 1.60

Maroon Bells

- Snowmass WA 271 1.19 1.27 1.15 1.21 Grand Canyon NP 285 2.12 1.50 1.18 1.60New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 7 NM SRC02 Unit # 350450902, PNM SJ #1

- 4: PM Only (PM = 3,884 TPY) Annual Average Natural Conditions Class I Area with at least 1 receptor within 300 km of source

Class I Area Minimum

Distance 98th Percentile for Each Year 98th

(km) 2001 2002 2003 3 year

AVG

Mesa Verde NP 40 0.86 0.96 1.13 0.98

Weminuche Wilderness 98 0.15 0.24 0.25 0.21

San Pedro Parks Wilderness 155 0.25 0.28 0.22 0.25

La Garita Wilderness 169 0.06 0.08 0.09 0.08 Canyonlands NP 170 0.28 0.20 0.22 0.23 Black Canyon Gunnison NM 203 0.09 0.11 0.07 0.09

Bandelier NM 210 0.13 0.19 0.17 0.16

Petrified Forest NP 213 0.05 0.03 0.05 0.05

West Elk Wilderness 216 0.07 0.09 0.07 0.08

Arches NP 222 0.19 0.19 0.15 0.17 Capitol Reef NP 232 0.12 0.07 0.09 0.09

Pecos Wilderness 248 0.08 0.10 0.10 0.09

Wheeler Peak Wilderness 258 0.07 0.06 0.07 0.06

Great Sand Dunes NM 269 0.07 0.05 0.06 0.06

Maroon Bells

- Snowmass WA 271 0.04 0.04 0.03 0.04 Grand Canyon NP 285 0.08 0.04 0.05 0.05

NM SRC02 Unit # 350450902, PNM SJ #1

- 4: NOx Only (NOx = 38,763 TPY) Annual Average Natural Conditions
Class I Area with at least 1 receptor within 300 km of source

Class I Area Minimum

Distance 98th Percentile for Each Year 98th

(km) 2001 2002 2003 3 year

AVG

Mesa Verde NP 40 3.59 3.73 3.24 3.52

Weminuche Wilderness 98 1.66 2.15 1.71 1.84

San Pedro Parks Wilderness 155 2.70 2.74 2.89 2.78

La Garita Wilderness 169 1.09 1.30 1.22 1.20 Canyonlands NP 170 4.28 3.22 2.79 3.43 Black Canyon Gunnison NM 203 1.67 1.72 1.86 1.75

Bandelier NM 210 1.69 2.13 2.23 2.02

Petrified Forest NP 213 0.80 0.70 0.30 0.60

West Elk Wilderness 216 1.22 1.44 1.60 1.42

Arches NP 222 3.22 2.50 2.40 2.71 Capitol Reef NP 232 2.89 0.92 1.45 1.75

Pecos Wilderness 248 1.49 1.72 1.94 1.72

Wheeler Peak Wilderness 258 1.15 1.09 1.36 1.20

Great Sand Dunes NM 269 1.09 1.00 1.10 1.07

Maroon Bells

- Snowmass WA 271 0.76 0.88 0.88 0.84 Grand Canyon NP 285 1.56 0.80 0.44 0.93New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 8 NM SRC02 Unit # 350450902, PNM SJ #1

- 4: SO 2 Only (SO 2 = 35,735 TPY) Annual Average Natural Conditions Class I Area with at least 1 receptor within 300 km of source

Class I Area Minimum

Distance 98th Percentile for Each Year 98th

(km) 2001 2002 2003 3 year

AVG

Mesa Verde NP 40 2.78 3.17 3.14 3.03

Weminuche Wilderness 98 1.28 1.23 0.89 1.13

San Pedro Parks Wilderness 155 1.77 2.13 1.72 1.87

La Garita Wilderness 169 0.81 0.89 0.70 0.80 Canyonlands NP 170 2.65 1.79 2.06 2.17 Black Canyon Gunnison NM 203 0.92 1.03 0.89 0.95

Bandelier NM 210 1.17 1.62 1.24 1.34

Petrified Forest NP 213 0.94 0.83 0.94 0.91

West Elk Wilderness 216 0.75 0.79 0.59 0.71

Arches NP 222 1.74 1.22 1.33 1.43 Capitol Reef NP 232 1.68 1.47 1.32 1.49

Pecos Wilderness 248 1.09 1.16 1.24 1.16

Wheeler Peak Wilderness 258 1.00 0.86 1.06 0.97

Great Sand Dunes NM 269 0.64 0.69 0.68 0.67

Maroon Bells

- Snowmass WA 271 0.54 0.62 0.36 0.51

Grand Canyon NP 285 1.18 0.78 0.73 0.90

NM SRC02 Unit # 350450902, PNM SJ #1

- 4: PM plus NOx (NOx = 38,763 TPY; PM = 3,884 TPY) Annual Average Natural Conditions Class I Area with at least 1 receptor within 300 km of source

Class I Area Minimum

Distance 98th Percentile for Each Year 98th

(km) 2001 2002 2003 3 year

AVG

Mesa Verde NP 40 4.27 4.06 3.46 3.93

Weminuche Wilderness 98 1.74 2.28 1.76 1.93

San Pedro Parks Wilderness 155 2.85 2.87 3.07 2.93

La Garita Wilderness 169 1.15 1.36 1.30 1.27 Canyonlands NP 170 4.39 3.33 2.91 3.54 Black Canyon Gunnison NM 203 1.73 1.84 1.90 1.82

Bandelier NM 210 1.77 2.29 2.31 2.12

Petrified Forest NP 213 0.83 0.72 0.31 0.62

West Elk Wilderness 216 1.26 1.50 1.64 1.47

Arches NP 222 3.30 2.65 2.50 2.82 Capitol Reef NP 232 3.06 0.95 1.50 1.83

Pecos Wilderness 248 1.55 1.77 2.04 1.79

Wheeler Peak Wilderness 258 1.20 1.12 1.40 1.24

Great Sand Dunes NM 269 1.14 1.05 1.15 1.11

Maroon Bells

- Snowmass WA 271 0.78 0.91 0.91 0.87 Grand Canyon NP 285 1.60 0.82 0.45 0.96New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 9 10.4 Summary of BART Determinations for San Juan

Clean Air Act § 169A(g)(7) directs States to consider five factors in making BART determinations. The regional haze rule codified these factors in 40 CFR § 51.308(e)(1)(ii)(B), which directs States to identify

the “ best system of continuous emissions control technology ” taking into account “ the technology available, the costs of compliance, the energy and non

- air quality environmental impacts of compliance, any pollution control equipment in use at the source, and the remai ning useful life of the source.”

The BART regulations define BART as meaning “ ...an emission limitation based on the degree of reduction achievable through the application of the best system of continuous emission reduction for each pol lutant which is emitted by ... [a BART

- eligible source]. ” In its guidance, EPA was clear that each State must determine the appropriate level of BART control for each source that is determined to be subject

- to

- BART. In making a BART determination, a State mu st consider the following factors:

(1) The costs of compliance; (2) The energy and non

- air quality environmental impacts of compliance; (3) Any existing pollution control technology in use at the source; (4) The remaining useful life of the source; and (5 ) The degree of improvement in visibility which may reasonably be anticipated to result from the use of such technology.

To consider these factors, New Mexico applied the following 5 step process as specified in the BART Guidelines at Appendix Y to 40 CFR Part 51:

Step 1

– Identify All Available Retrofit Control Technologies Step 2

– Eliminate Technically Infeasible Options Step 3

– Evaluate Control Effectiveness of Remaining Control Technologies Step 4

– Evaluate Impacts and Document the Results a) Costs of Compliance b) Energy Impacts c) Air quality environmental impacts d) Non

- air environmental impacts e) Remaining useful life Step 5

– Evaluate Visibility Impacts

The Department applied the 5 step process to San Juan, as described in detail in Appendix D. The results

are summarized below.

10.4.1 Particulate Matter

Based on the five factor analysis, the Department determined in 2011 that BART for Units 1

- 4 for particulate matter (“ PM ”) is the existing pulse jet fabric filter control technology and an existing emission

rate of 0.015 lb/ MMBtu . The Department’s determination of BART was based on the following results of the full five factor analysis:

1. Each of Units 1

- 4 is equipped with a pulse jet fabric filter (PJFF) and is subject to a federally

enforceable emission lim it of 0.015 lb PM/ MMBtu

.

2. The Department reviewed both the cost

- effectiveness and incremental cost

- effectiveness of additional control technology (WESP) and found these costs to be excessive.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 10 3. There are no non

- air impacts associated with the WESP technolog y.

4. There are additional energy impacts associated with the WESP technology and the Department

considers these costs to be reasonable.

5. The Department reviewed the visibility improvement that resulted from the installation of the consent decree technology (PJFF and LNB/OFA) and that would result from the addition of WESP technology. The Department determined that on a facility

- wide basis the visibility improved by 1.06 deciviews (dv) from the installation of the consent decree technology at Mesa

Verde Natio nal Park (Mesa Verde). The installation of WESP would result in a facility

- wide improvement of 0.62 dv at Mesa Verde.

On November 27, 2012, the EPA approved New Mexico’s determination that PJFF is BART for PM at

San Juan . 77 Fed. Reg. 36,044

. Notwithsta nding the fact that the BART requirement has thus been satisfied with respect to PM , additional PM reductions will be made at the San Juan Generating Station

under the “State Alternative” described below.

10.4.2 Nitrogen Oxides

Based on the five factor ana lysis, the Department determined in 2011 that BART for Units 1

- 4 for NOx is SNCR technology and an emission rate of 0.23 lb/ MMBtu on a 30

- day rolling average. The Department’s determination of BART was based on the following results of the five factor anal ysis:

1. SNCR technology is considered cost

- effective at an average cost of $3,494 dollars per ton of NOx removed. SNCR technology will reduce the facility annual NOx emissions by 4,900 tons.

2. The SNCR technology will result in additional energy impacts and non

- air impacts. The SNCR technology will require a new reagent system and a reagent storage system. The Department

considered these additional costs in the review of the overall cost

- effectiveness of SNCR and

found these costs to be reasonable.

3. The Depar tment reviewed the visibility improvement that resulted from the installation of the SNCR technology. The Department determined that on a facility

- wide basis the visibility improved by 0.25 dv at San Pedro Parks, 0.22 dv at Mesa Verde, and 0.21 at Bandelie r.

4. An emission limit of 0.23 lb NOx/ MMBtu at each of Units 1

- 4 equals the EPA’s established presumptive limit for dry

- bottom, wall

- fired boilers burning sub

- bituminous coal.

5. The Department reviewed additional economic information provided by PNM that analyzed the economic impact to ratepayers in New Mexico. PNM estimates indicate the cost of control technology beyond SNCR would be financially burdensome and cause economic hard ship to low

income New Mexicans. According to the U.S. Census Bureau, as of 2009, 18 percent of New Mexicans were living below the poverty line, as defined by the federal poverty standards. PNM estimates a rate increase of $11.50 per year per residential r atepayer from the installation of SNCR versus an estimated rate increase of $82.00 per year from the installation of SCR.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 11 The visibility improvement projected for each Class I area from the installation of various NOx control technologies is shown in Figure 10

- 1

.

Figure 10

- 1 : Visibility Improvement from NOx BART Controls at San Juan Generating Station

Notwithstanding this 2011 NOx BART determination applicable to all four units, which the Department believes would satisfy all applicable requirements, the Department has determined that the State Alternative would result in additional visibility improvements and other air and non

- air benefits, as described below, and therefore is pr eferable to the 2011 NOx BART determination.

10. 4.3 State Alternative

As noted in the Introduction above, on February 15, 2013, New Mexico, EPA, and PNM signed a

tentative agreement (Term Sheet) to address the CAA requirements for regional haze and interstate transport for visibility at the San Juan Generating Station. Although the agreement arose from a dispute over the NOx BART determination, its terms will also result in reduction of PM, SO 2 , and other pollutants including greenhouse gases.

In a ccordance with the Term Sheet, PNM submitted to the Department in March 2013 a revised 5

- factor BART analysis that includes consideration of the State Alternative including voluntary unit retirements as a new alternative operating scenario that had not pre viously been analyzed . As documented in AppendixNew Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 12 D of this SIP , the Department has reviewed the revised BART analysis, and has determined that the State

Alternative satisfies the BART requirements of the CAA and 40 C.F.R Part 51 Appendix Y.

The compari son of the State Alternative (SNCR on Units 1 and 4 and the shutdown of Units 2 and 3, or 2 SNCR/2 Shutdown) to the Department's 2011 BART determination of SNCR on all four units (4 SNCR)

and the installation of SCR on all four units (4 SCR) (EPA's Federal Implementation Plan decision; 76 FR 52388, August 22, 2011) is summarized in Table 10

- 3.

Table 1 0

- 3: Facility

- Wide Pollutant Emissions from [ State Alternative, FIP and NMED SIP ] 2 SNCR/2 Shutdown, 4 SNCR and 4 SCR Scenarios

Scenario NOx SO 2 PM CO CO 2 VOC Mercury Non

Hg Acid

Gases

Current 21,000 10,500 2,380 33,507 14,669,968 210 0.0842 5.4 1,488
[ State Alternative ] 2 SNCR/2 Shutdown 8,011 3,483 1,184 18,615 7,314,801 104 0.042 2.7 744

[ State Alternative ] 2 SNCR/2 Shutdown

% Reduction 62% 67% 50% 44% 50% 50% 50% 50% 50%

[ NMED SIP ]

4 SNCR 16,100 10,500 2,380 33,507 14,699,968 210 0.0842 5.4 1,488

[ NMED SIP ]

4 SNCR

% Reduction 23% 0% 0% 0% 0% 0% 0% 0% 0%

[ EPA FIP ]

4 SCR 3,502 10,500 2,380 33,507 14,699,968 210 0.0842 5.4 1,488

[ EPA FIP ]

4 SCR

% Reduction 83% 0% 0% 0% 0% 0% 0% 0% 0%

Visibility improvements were compared for the current configuration (Baseline), [ NMED SIP assessment (SNCR on all four units, the EPA FIP final determination (SCR on all four units), and the State

Alternative Plan ] 4 SNCR

, 4 SCR , and 2 SNCR/2 Shutdown . Figure 10

- 2 shows the differences in visibility between the alternatives at the 16 Class I areas within 300 kilometers of SJGS. Table 10

- 4 shows the average visibility improvement for the ye ars 2001

- 2003 for the 4 SCR, 4 SNCR and 2 SNCR/2

Shutdown scenarios. The [ State Alternative Plan ] 2 SNCR/2 Shutdown scenario provides similar visibility improvement as the [ EPA FIP plan ] 4 SCR scenario . See Appendix D for additional details.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 13 Table 10

- 4: 2001

- 2003 Average Visibility Improvement for 4 SCR, 4 SNCR and 2 SNCR/2

Shutdown Scenarios

Class I Area 4 SCR 4 SNCR 2 SNCR/2

Shutdown Difference Difference 4 SCR to 2 SNCR/2

Shutdown 4 SCR to 4

SNCR

Arches 1.06 0.37 0.97 0.69 0.09

Bandelier 0.61 0.23 0.64 0.38

- 0.03

Black Canyon 0.37 0.16 0.41 0.21

- 0.04

Canyonlands 1.54 0.48 1.38 1.06 0.16

Capitol Reef 0.34 0.10 0.42 0.24

- 0.08

Grand Canyon 0.18 0.08 0.25 0.10

- 0.07

Great Sand Dunes 0.73 0.27 0.69 0.46 0.04

La Garita 0.78 0.29 0.73 0.49 0.05

Maroon Bells 0.20 0.07 0.22 0.13

- 0.02

Mesa Verde 2.69 0.55 2.41 2.14 0.28

Pecos 0.70 0.25 0.66 0.45 0.04

Petrified Forest 0.16 0.07 0.25 0.09

- 0.09

San Pedro 1.41 0.49 1.29 0.92 0.12

West Elk 0.45 0.17 0.43 0.28 0.02

Weminuche 1.29 0.41 1.23 0.88 0.06

Wheeler Peak 0.59 0.24 0.58 0.35 0.01New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 14 Figure 1 0

- 2: Comparison of Visibility Improvement of Alternatives at San Juan Generating Station

Note: WHPE

– Wheeler Peak Wilderness Area, NM; WEMI

– Weminuche Wilderness Area, CO; WEEL

– West Elk Wilderness Area, CO; San Pedro Parks Wilderness Area

– NM; PEFO

– Petrified Forest National Park, AZ; PECO

– Pecos Wilderness Area,
NM; MEVE

– Mesa Verde National Park, CO; MABE

– Maroon Bells Wilderness Area, CO; LAGA

– La Garita Wilderness
Area, CO; GRSA

– Great Sand Dunes National Monument, CO; GRCA

– Grand Canyon National Park, AZ; CARE

– Capitol Reef National Park, UT; CANY

– Canyonlands National Park, UT; BLCA

– Black Canyon of the Gunnison National Park, CO;

BAND

– Bandelier Wilderness Area, NM; ARCH

– Arches National Park, UT

[ Based on this analysis, the Department determines that the State Alternative is superior to the 2011 NOx BART SIP and EPA’s NOx BART FIP for the following reasons: ] The Department conside red the terms

of the non

- binding agreement between the EPA, NMED and PNM, signed February 15, 2013 (the “State Alternative”), and the resulting significant environmental improvements of this alternative and compared

this scenario to the 4 SNCR and 4 SCR sc enarios previously evaluated. The Department’s determination of BART was based on consideration of the BART statutory factors in the context of the following elements of the State Alternative (2 SNCR/2 Shutdown).

1) PNM will retire Units 2 and 3 by December 31, 2017. These retirements do not give rise to control equipment costs requiring amortization. The remaining useful life of the source is defined as 30 years for the three scenarios described (4 SCR, 4 SNCR, 2 SNCR/2 Shutdown). Therefore, the statutory factor of the remaining useful life of the source does not weigh in favor of any option

over another.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 15 2) PNM will obtain the necessary construction permit modification to limit the SO 2 emission rates at Units 1 and 4 to 0.10 lb/MMBtu on a daily rolling 30

- d ay average basis. These SO 2 emission reductions occur separately and apart from the SO 2 backstop trading program that EPA has already approved as satisfying BART. In addition to increased visibility improvement, these SO 2 reductions will lead to non

- air q uality environmental benefits, such as decreased acid deposition.

3) T he retirement of Units 2 and 3 will reduce the facility annual NOx emissions by an additional
10,550 tons. When added to the controlled emission rate of Units and 1 and 4, total annual NOx emission will be reduced by 12,989 tons. Additionally, PNM will conduct performance testing to determine if the SNCRs installed on Units 1 and 4 can achieve significantly l ess than 0.23

lb/MMBtu.

4) [ The retirement of Units 2 and 3 will reduce raw material usage at the facility, including limestone, activated carbon, coal and No. 2 diesel oil. See Table below. ] The 2 SNCR/2 Shutdown scenario would result in less material usage than the 4 SCR and 4 SNCR scenarios. See Table 23. This will result in less limestone required to be transported and mined, less diesel fuel that would need to be refined for this power plant, less coal mined and less carbon that would need to be activate d. Closure of two units will result in up to 53 percent less water used, from 21,000 acre

- feet to
10,161 acre

- feet; wastewater generated will be reduced by up to 50 percent, from 41 million gallons to 21 million gallons; and solid waste generated will be r educed by up to 50 percent, from 1.71 million tons per year to 854,130 tons per year.

Table 23: Raw Material Usage Comparison

Raw Material 2 SNCR/2

Shutdown (TPY) Baseline, 4 SNCR, and 4

SCR

Limestone (1) 86,052 172,104

Activated Carbon (1) 130 261

Coal (2) 2,667,364 5,334,729

No. 2 Diesel Oil (2) 1,007,336 2,014,671
(1) Based on 2012 material usage data

. (2) Based on 2011 material usage data

.

The energy and non

- air quality environmental benefit of these resource savings weighs heavily in

favor of the 2 SNCR/2 Shutdown scenario over the 4 SCR and 4 SNCR scenarios.

5) The two

- unit retirement scenario will result in a substantial decrease in particulate matter emissions from coal processing, handling and transportation, as well as a substantial reduction in greenhou se gas emissions, mercury and [ non mercury ] other hazardous air pollutant emissions, and acid gas emissions as detailed i n Table [ 22 ] 24 below. The non

- air quality environmental benefits of these reductions, such as less impact on climate and less depositi on of mercury to waterways, weigh heavily in favor of the 2 SNCR/2 Shutdown scenario

.

[ 6) Water usage is expected to drop by up to approximately 53% to 10,161 acre

- feet/year. ]

6) Table 22 shows the average visibility improvement [ from the State Alternative ] between the three scenarios of 4 SCR, 4 SNCR and 2 SNCR/2 unit shutdown. The 2 SNCR/2 Shutdown scenario achieves significant visibility improvements as compared to the baseline and [ the SNCR ]

installation of SNCR on Units 1

- 4. The visibility improvemen ts from the State Alternative ofNew Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 16 SNCR on two [ unit retirement and 2 SNCR installation scenario compared ] units and two units shutdown compare very closely with the SCR installation scenario as [ proposed ] contained in the FIP (less than [ 0.5 dv ] 0.3 dv impact at any Class I area ). For the 4 SCR and 2 SNCR/2 Shutdown scenarios, the average difference over three years is 0.28 dv at Mesa Verde and 0.16 dv at Canyonlands.

Therefore, with respect to the statutory factor of the degree of visibility improve ment anticipated, the 2 SNCR/2 unit shutdown scenario is superior to the 4 SCR scenario, and substantially equivalent to the 4 SCR scenario.

7) Table 10 includes the cost in dollars per ton for SCR and SNCR, as well as other scenarios. T he total capital inve stment of the [ proposed ] FIP 4 SCR scenario is estimated at nearly $861,871,000, as compared to $34,556,000 for the installation of SNCR at Units 1 and 4. This additional and significant capital expenditure that would be required to comply with the [ FIP ] 4 SCR scenario is not justified given the slight [ and undetectable ] improvement in visibility of the 4 SCR scenario

over the 2 SCR/2 Shutdown scenario

.

8) Finally, with respect to the statutory requirement to consider existing pollution controls at the

sourc e, such existing pollution control equipment was evaluated for all alternatives beginning in Step 1 of the analysis, and is outlined in Table 10. NMED determined that existing control equipment is not sufficient to meet BART requirements for NOx at San Jua n Generating Station. This factor has no further relevance in selecting among th e control options in this case

.

[ Accordingly, the State Alternative is hereby adopted in lieu of the 2011 NOx BART determination, to be implemented as provided in section 10. 5 below. ]

Weighing all the above considerations as required by CAA § 169A, the Department has determined that the State Alternative (2 SNCR/2 Shutdown), which achieves substantial environmental benefits beyond the requirements of the FIP (4 SCR), the SIP (4 SNCR) and the requirements of the BART Guidelines at 40 CFR Part 51 Appendix Y at a significantly lower cost than the FIP scenario of 4 SCRs, satisfies the statutory and regulatory requirements of BART.

10.5 Implementation of the State Alternative

In accordance with 40 CFR § 51.308(e)(1)(iv), the Department determines that the schedule provided in the Term Sheet will result in the installation of BART controls as expeditiously as practicable. Therefore,

in accordance with the Term Sheet, the following requirements apply to the San Juan Generating Station

.

a. Fifteen (15) months after EPA final approval of this revised SIP, no earlier than January 31, 2016, Public Service Company of New Mexico (PNM) will complete installation of selective non

catalytic reduction (SNCR) technology on SJGS Unit 1 and 4 of no grea ter than 0.23 lb/MMBtu on a daily rolling 30

- day average basis.

b. Testing Program

. PNM shall comply with the following. Dates that follow with an asterisk(*) in items (i)

– (iv) shall be revised accordingly if the installation date extends past January 3 1, 2016 due to delay in EPA’s SIP approval :

i. PNM will commence a program of testing and evaluation, after the installation of the SNCRs. The Testing Program consisting of SNCR Performance Testing, Fuel Performance Testing,New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 17 and Long

- Term Performance Evaluat ion is to be completed no later than January 31, 2017, * unless the Long

- Term Performance Evaluation is delayed per the language in paragraph b.iv

below

.

ii. SNCR Performance Testin g will be conducted to develop a targeted ammonia/urea injection

rate range at various load levels without exceeding a to

- be

- agreed

- upon preliminary slip limit of between 5 and 10 ppm, with the goal of minimizing NOx emissions. PNM shall provide the results of the performance tests, recommended final slip limit, and target ammonia/u rea injection rates to NMED and EPA by April 1, 2016. * PNM will allow up to April 30, 2016 * for the agencies to either concur with PNM’s slip limit recommendation or to concur on a different slip limit that PNM will comply with for Units 1 and 4.

iii. P NM will conduct Fuel Performance Testing (in conjunction with the SNCR Performance Testing) of its pre

- treated coal technology, so long as it has not been previously determined to result in any detrimental effect to SJGS Units 1 and 4 or their operation, with the objective of further reducing NOx emissions. If the Fuel Performance Testing demonstrates that it does not: (i) measurably increase NOx emissions, or (ii) adversely impact overall unit operations, PNM shall also use such pre

- treated coal for the 9

- month L ong

- Term Performance Evaluation Period described below. PNM will also use pre

- treated coal on units 2 and 3 when

used on units 1 and 4.

iv. Long

- Term Performance Evaluation Period. PNM will begin collecting NOx emission and ammonia/urea injection rate data from Units 1 and 4 on a daily rolling 30

- day average basis for nine continuous months beginning on May 1, 2016 * and provide such data and any recommendations on the NOx emission limit to NMED and EPA by February 28, 2017 * or no later than 28 days after completing the Long

- Term Performance Evaluation Period. PNM may request more time if a slip limit is not agreed upon by April 30, 2016. * The Long

- Term Performance Evaluation Period must include 60 days between June 1 st and August 30 th and 60 days between December 1 st and February 28 th . The Demonstrated Emission Rate will be the highest daily rolling 30

- day average emission rate during the 9

- month Long

- Term Performance Evaluation Period (not including periods of malfunction or abnormal operating conditions) adjusted to three significant digits. If the Demonstrated Emission Rate is greater than or equal to 0.200 lb/ MMBtu on a daily rolling 30

- day average basis no adjustment to the

NOx emission rate for units 1 and 4 will be ma de. If the Demonstrated Emission Rate is less than 0.200 lb/MMBtu on a daily rolling 30

- day average basis PNM will apply for a permit modification by March 31, 2017 * (or no later than 60 days after completing the Long

- Term Performance Evaluation Period) to reduce the permitted emission rate by 60% of the

difference between 0.23 lb/MMBtu and the Demonstrated Emission Rate, provided the revised emission rate does not adversely impact overall unit operations. The permit modification will include the agreed up on ammonia slip limit.

c. No later than six months from the Board’s adoption this SIP revision, PNM will comply with a sulfur dioxide (“ SO 2 ” ) emission rates at Units 1 and 4 of 0.10 lb/MMBtu on a daily rolling 30

- day average basis.

d. PNM shall diligently se ek all necessary regulatory approvals to allow for retirement of SJGS

Unit s 2 and 3 by December 31, 2017, and if such approvals are granted, shall retire SJGS Units 2 and 3 by December 31, 2017.New Mexico Section 309(g) Regional Haze SIP
June 2, 2011; Revision to Chapter 10, June 27, 2013 Public Review Draft pg. 10

- 18 e. Nothing in this SIP shall relieve the SJGS from its oblig ations to comply with all applicable federal, state, and local laws and regulations, including laws, regulations, and compliance deadlines that become applicable after the date that this SIP revision is approved by EPA.

In accordance with 40 CFR § 51.308(e)(1) (v)

, San Juan Generating Station shall maintain the control equipment required by this chapter and establish procedures to ensure such equipment is properly operated and maintained.