reviewing ADEQ Title V permitting decision
How later courts described this case
- reviewing ADEQ Title V permitting decision
Written by the judges who cited it.
The opinion
Cite as 2015 Ark. App. 703
ARKANSAS COURT OF APPEALS
DIVISION IV
CV-14-699
No.
NUCOR STEEL-ARKANSAS AND Opinion Delivered: DECEMBER 9, 2015
NUCOR-YAMATO STEEL
COMPANY APPEAL FROM THE ARKANSAS
APPELLANTS POLLUTION CONTROL AND
ECOLOGY COMMISSION
V. [NO. 13-006-P]
ARKANSAS POLLUTION
CONTROL & ECOLOGY
COMMISSION AND BIG RIVER
STEEL, LLC
APPELLEES AFFIRMED
KENNETH S. HIXSON, Judge
In this environmental-law case, the Arkansas Department of Environmental Quality
(“ADEQ”) issued a permit allowing appellee Big River Steel, LLC (“BRS”) to build and
operate a new steel mill in Mississippi County, Arkansas. Appellants Nucor Steel-Arkansas
and Nucor-Yamato Steel Company (collectively, “Nucor”), who also own steel mills in
Mississippi County, opposed the permit and appealed ADEQ’s decision to the Arkansas
Pollution Control and Ecology Commission (“PC&E”). PC&E affirmed the permit, and
Nucor sought judicial review in the Mississippi County Circuit Court. That court, upon a
motion by BRS, transferred the case to the Arkansas Court of Appeals, pursuant to Arkansas
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Code Annotated section 8-4-223(d) (Supp. 2015). The operative decision before us is the
administrative ruling of PC&E, and we affirm PC&E’s decision.
I. Background
The BRS permit was issued under the terms of the federal Clean Air Act, which
ensures that economic growth will occur in a manner consistent with the preservation of
clean air. See 42 U.S.C. § 7401 et seq. (2014). The Act particularly addresses the pollution
dangers posed by “major emitting facilities,” such as the BRS steel mill in this case. These
types of facilities are subject to a pre-construction review and may not be built unless, among
other things, a permit has been issued containing emission limitations; the permit has
undergone a regulatory evaluation; the facility demonstrates that it will employ the best
available pollution-control technology; and the facility demonstrates that its emissions
will not cause or contribute to excessive air pollution. 42 U.S.C. § 7475 (2014). The
preconstruction review is referred to as Prevention of Significant Deterioration (PSD),
meaning that it seeks to prevent significant deterioration of the air quality around the
proposed construction site.
Under the Clean Air Act and its attendant regulations, the responsibility for the PSD
process is shared by state and federal governments. State regulators are charged with
conducting the necessary review of PSD applications and issuing the construction and
operating permits. In Arkansas, the permitting authority is ADEQ. Ark. Code Ann. § 8-4-
203(a) (Supp. 2015). Federal regulators are responsible for establishing air-quality standards,
which set limits on the amount of pollution that will be tolerated in a given region. Toward
that end, the Environmental Protection Agency (“EPA”) has instituted National Ambient
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Air Quality Standards (NAAQS) for certain “criteria” pollutants, which are the most
common air pollutants found in the United States. See 42 U.S.C. § 7409 (2014); 40 C.F.R.
Part 50. Included among the criteria pollutants are the small, fine smoke particles designated
as PM2.5 (particulate matter with a diameter of 2.5 microns or less). As of March 2013, the
EPA’s primary annual air-quality standard for PM2.5 was twelve micrograms per cubic meter
of air (12 µg/m3).
In January 2013, BRS filed a PSD application with ADEQ to construct and operate
a new steel mill near Osceola in Mississippi County. The application stated that the mill
would produce up to 3.4 million short tons per year of rolled steel products and would
employ two electric arc furnaces and various other components, some of which would be
natural-gas fired. Subsequent to its initial application, BRS submitted revised applications in
March and June 2013 and asked that its application be processed in “an accelerated timely
manner.”
As required by law, BRS’s application included an air-quality analysis, the purpose
of which was to demonstrate that the new mill would not have an adverse impact on air
quality in the region. Because the mill had not yet been constructed, BRS could only
estimate the types and concentrations of pollutants that would be discharged once the mill
was operational. To properly estimate the concentration of air pollutants, BRS employed a
technique referred to as air-dispersion modeling. Modeling is a complex process that, among
other things, uses computer inputs to predict the future emissions of a planned industrial
facility. The modeling results, when added to the existing emissions from other nearby
plants, yield the concentration of pollutants that will be released into the region’s ambient
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air by industrial means. An air-quality analysis must also account for the “background”
pollution that exists in the area due to agricultural, vehicular, or other activities. Background
pollution is ordinarily measured by a monitor in place at the proposed construction site.
However, no such monitor existed in Mississippi County. BRS therefore utilized a
“representative” background monitor in Dyersburg, Tennessee, approximately forty miles
to the northeast.
BRS’s modeling, along with ADEQ’s confirmatory modeling, predicted that the new
mill and its neighboring facilities would emit a PM2.5 concentration of approximately 2.56
µg/m3. This figure, when combined with a reading of 9.44 µg/m3 from the Dyersburg
background monitor, demonstrated an exceedance or near-exceedance of the 12 µg/m3
federal ceiling for PM2.5. BRS reviewed its data and determined that it could properly reduce
some of the inputs it had utilized in its initial modeling run. BRS then repeated the modeling
and arrived at a PM2.5 level of 11.91 µg/m3—just below the 12 µg/m3 standard. This final
air-quality analysis was submitted to ADEQ on June 24, 2015.
The next day, ADEQ issued a Draft Permit that, if finalized, would allow BRS to
construct and operate the new mill. 1 The lengthy and data-rich Draft Permit included BRS’s
most recent air-quality analysis results for PM2.5. The Draft Permit also required BRS to
apply specific pollution-control technology to its emissions from all plant “sources,” such as
1
Once PSD requirements are met and the facility has been constructed, the applicant
may receive an operating permit pursuant to Title V of the Clean Air Act. Arkansas has a
unified permit process in which the PSD and Title V permit applications are considered
simultaneously.
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smokestacks and vents; set forth exact emission limits for each pollutant discharged by each
source; and imposed requirements for post-construction testing and monitoring.
The issuance of the Draft Permit triggered a thirty-day public-comment period,
during which BRS, the EPA, and any interested third party could present ADEQ with
written comments about the draft. Ark. Code Ann. § 8-4-203(e) (Supp. 2015). Appellant
Nucor, who had actively followed BRS’s application, submitted over forty comments, most
objecting to the technical aspects of BRS’s modeling and to a perceived bias in ADEQ’s
evaluation of BRS’s application. After reviewing the public comments, ADEQ modified
the Draft Permit in some respects, then issued a Final Permit on September 18, 2013. Nucor
appealed ADEQ’s decision to PC&E pursuant to Arkansas Code Annotated section 8-4-
205(b)(1) (Supp. 2015).
II. Appeal to PC&E
Nucor’s petition to PC&E cited approximately thirty errors that allegedly occurred
during the permitting process. Upon receiving the petition, PC&E appointed an
administrative hearing officer (AHO) to review Nucor’s allegations and conduct the
necessary proceedings. See Ark. Code Ann. § 8-1-204 (Supp. 2015) (allowing PC&E to
employ an administrative hearing officer). Preliminarily, the AHO dismissed several of
Nucor’s allegations due to procedural deficiencies, such as the failure to raise them in the
public comments. See Ark. Code Ann. § 8-4-205(b)(2) (Supp. 2015). The remaining issues
proceeded to an adjudicatory hearing.
In anticipation of the hearing, Nucor submitted pre-filed testimony from its manager
of environmental affairs, Jeffrey Braun, and from three expert witnesses: Yousheng Zeng;
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George Schewe; and Kenneth Weiss. In opposition to Nucor, BRS submitted pre-filed
testimony from its consultant, Steven Frey, and from its expert witness, Gale Hoffnagle.
ADEQ provided pre-filed testimony from its permit writer/engineer, Shawn Hutchings,
and its Air Permit Branch Manager, Thomas Rheaume. In addition to giving pre-filed
testimony, these witnesses, along with ADEQ Director Teresa Marks, testified in person at
the adjudicatory hearing, which was held over a four-day period in February 2014. The
substance of the witnesses’ testimony will be discussed later in this opinion, in connection
with the arguments on appeal. But, essentially, Nucor’s experts testified, inter alia, that BRS
was not justified in using Dyersburg, Tennessee as a representative monitor for background
PM2.5; that ADEQ’s review of BRS’s application was superficial and unsatisfactory; that
BRS and ADEQ ignored certain inputs or used incorrect inputs in the modeling process;
and that proper modeling would have shown an exceedance of the air-quality standards for
PM2.5. BRS and ADEQ witnesses, by contrast, testified that Dyersburg, Tennessee was a
proper representative site for background PM2.5 and that all legal requirements for modeling
and ADEQ review were otherwise met.
Following the hearing, the AHO issued a recommended decision on March 20, 2014.
See Ark. Code Ann. § 8-1-203(c)(2) (Supp. 2015) (requiring the AHO to administer the
hearing and, after due deliberation, submit a recommended decision to the Commission).
The AHO’s recommended decision covered sixty-nine pages, discussed the evidence and
the parties’ arguments at length, and counseled affirmance of the BRS permit. Nucor
responded with a request for oral argument before PC&E’s Commissioners, challenging
virtually every aspect of the AHO’s recommended decision. After a brief oral argument on
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April 25, 2014, the Commissioners voted to adopt the AHO’s decision. That same day,
PC&E issued a minute order affirming the BRS permit and adopting and affirming the
AHO’s recommended decision in full. Nucor then appealed to the Mississippi County
Circuit Court, pursuant to Arkansas Code Annotated sections 8-4-222 and -223(a) (Supp.
2015).
III. Judicial Review
Once the case arrived in circuit court, BRS filed a motion to transfer the appeal to
the Arkansas Court of Appeals, pursuant to the recently enacted Arkansas Code Annotated
section 8-4-223(d). This statute provides that, upon the filing of a motion by the owner of
the business involved in the permit process, an appeal to circuit court “shall be transferred
to the Arkansas Court of Appeals.” The Mississippi County Circuit Court granted the
transfer, bringing the current appeal before this court. We begin by addressing Nucor’s
arguments concerning our standard of review.
IV. Standard of Review
Nucor’s first argument is that our court should review PC&E’s decision “sitting
essentially as a circuit court.” This argument stems from the above-mentioned section 8-4-
223(d), which allows a “bypass” of the circuit court in favor of a direct transfer to the
Arkansas Court of Appeals. We do not interpret the statute as requiring our court to act as
a circuit court.
Section 8-4-223(d) was enacted as part of Act 1021 of 2013. The Act’s preamble
states that its purpose was, in part, to allow a “direct appeal” to the Arkansas Court of
Appeals in order to “streamline” the review of PC&E rulings. When interpreting a
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legislative enactment, our courts have looked to the preamble of an act to determine its
purpose and intent. See Okla Homer Smith Furn. Mfg. Co. v. Larson & Wear, Inc., 278 Ark.
467, 646 S.W.2d 696 (1983); Two Bros. Farm, Inc. v. Riceland Foods, Inc., 57 Ark. App. 25,
940 S.W.2d 889 (1997). In light of the preamble to Act 1021, the only reasonable
interpretation of section 8-4-223(d) is that it was intended simply to expedite the process of
bringing a PC&E ruling forward for appellate review. We discern no intent to divest the
appellate court of its ordinary function or to have it assume the posture of a circuit court.
Nucor points out that, had the appeal from PC&E’s ruling remained in circuit court,
that court could have allowed Nucor to present additional testimony. See Ark. Code Ann.
§ 8-4-227(c)(1)(B) (Supp. 2015). Accordingly, Nucor has asked this court to preserve that
opportunity and to allow discovery for the purpose of developing additional evidence. This
same request was presented to our court in several motions filed prior to the submission of
the case. At that time, we rejected Nucor’s request and denied its motion for
reconsideration. 2 We stand by our rulings on Nucor’s motions.
It is correct that Arkansas Code Annotated section 8-4-227(c)(1)(B) grants authority
to the circuit court to hear additional evidence. See Act 1021 of 2013, § 7. However, that
statute does not grant the same authority to the appellate court. As discussed above, we will
review this matter as an appellate court, and not as a circuit court. So, while we understand
2
Our supreme court also denied Nucor’s petition for a writ of certiorari directed to
this court.
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Nucor’s concern over losing the opportunity to present additional evidence, we decline to
revisit this issue. 3
Next, Nucor argues that our court should review PC&E’s ruling de novo. We
decline to do so. It is not our role in an administrative appeal to conduct a de novo review
of the record. See Ark. Bev. Retailers Ass’n v. Langley, 2009 Ark. 187, 305 S.W.3d 427.
Rather, we review administrative appeals with great deference to the agency’s expertise,
based on our recognition that such agencies are better equipped by specialization, insight
through experience, and more flexible procedures to determine and analyze legal issues
affecting them. See Pine Bluff for Safe Disposal v. Ark. Pollution Control & Ecology Comm’n,
354 Ark. 563, 127 S.W.3d 509 (2003). Agency decisions will be upheld if they are supported
by substantial evidence and are not arbitrary, capricious, or characterized by an abuse of
discretion. Id. On appeal, we give the evidence its strongest probative force in favor of the
agency’s findings. Id. Even where issues of law are concerned, we often accord deference to
the agency’s ruling, particularly when reviewing the agency’s interpretation of statutes or its
own rules and regulations. See Lamar Outdoor Advert. v. Ark. Hwy. & Transp. Dep’t, 86 Ark.
App. 279, 184 S.W.3d 461 (2004).
Given the above authorities, a de novo review is not appropriate in this appeal from
an administrative agency. Furthermore, a de novo review would be inconsistent with
Arkansas Code Annotated section 8-4-229 (Repl. 2011), which provides that, in any appeal
involving a PC&E order, the agency’s action shall be “prima facie evidence reasonable and
We note that Nucor does not develop an argument as to the constitutionality of
3
section 8-4-223(d).
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valid.” The same statute provides that all findings of fact by PC&E shall be prima facie
evidence of the matters stated therein and that the burden of proving the contrary shall be
upon the appellant. This statute unquestionably requires a deferential review of PC&E
rulings, which is inconsistent with a de novo review.
Nucor nevertheless maintains that the separation-of-powers doctrine requires us to
conduct a de novo review because PC&E’s ruling constituted a quasi-judicial act. See City
of Ft. Smith v. McCutchen, 372 Ark. 541, 279 S.W.3d 78 (2008) (holding that, while a court
may not conduct a de novo review when an administrative agency has acted in a legislative
or executive capacity, a court may conduct a de novo review of an agency’s quasi-judicial
ruling). Here, PC&E’s ruling on the issuance of a regulatory permit was an exercise of
executive function, hinging on executive discretion, and was not a quasi-judicial ruling. See
Enviroclean, Inc. v. Ark. Pollution Control & Ecology Comm’n, 314 Ark. 98, 858 S.W.2d 116
(1993); Ark. Comm’n on Pollution Control & Ecology v. Land Developers, Inc., 284 Ark. 179,
680 S.W.2d 909 (1984). Thus, a de novo review would be improper. McCutchen, supra. The
traditional, limited standard of review utilized in administrative appeals therefore applies. See
La. v. Joint Pipeline Grp., 2010 Ark. 374, 373 S.W.3d 292; Tri-County Solid Waste Dist. v.
Ark. Pollution Control & Ecology Comm’n, 365 Ark. 368, 230 S.W.3d 545 (2006).
V. Procedural Matters During PC&E Review
Nucor contends next that PC&E committed several procedural errors in its review
of the ADEQ permit decision. First, Nucor argues that PC&E did not conduct a de novo
review as required by Arkansas Code Annotated section 8-1-203(c)(3)(A)(i) & (ii) (Supp.
2015). We see no error. As allowed by law, PC&E appointed the AHO to conduct a review
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of ADEQ’s permit decision. The AHO duly received testimonial and documentary
evidence and carried out a de novo review based on that proof. In doing so, the AHO acted
as PC&E’s agent, Ark. Code Ann. § 8-1-203(c)(1) (Supp. 2015), and therefore met the
requirements of the law on behalf of PC&E.
Nucor insists, however, that PC&E’s minute order, which adopted the AHO’s
recommended decision, should have set forth specific findings of fact. No statute requires
this. Moreover, Nucor’s analogy to Workers’ Compensation law on this point is not well
founded. The Workers’ Compensation Commission may adopt its ALJ’s findings and
conclusions, thereby making those findings and conclusions its own. See Curt Bean Transp.,
Inc. v. Hill, 2009 Ark. App. 760, 348 S.W.3d 56.
Taking another approach, Nucor argues that PC&E’s Commissioners could not
possibly have familiarized themselves with the AHO’s recommended decision and his
voluminous record because the PC&E minute order was issued only eight days after closing
briefs were filed by the parties. It appears to us that the Commissioners had more than eight
days in which to assess and understand the materials in the case—PC&E had earlier received
the AHO’s detailed decision and Nucor’s request for oral argument, which was over 100
pages in length and meticulously explained Nucor’s arguments for reversal of the permit.
Regardless, we decline to speculate on the length of time required for the Commissioners
to render their decision.
Next, Nucor argues that the AHO imposed an erroneous burden of proof during
the adjudicatory hearing. The AHO correctly stated that Nucor had the burden of proving
by a preponderance of the evidence that BRS’s permit did not meet the requirements of
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the law. See Ark. PC&E Reg. 8.616(B). And, on appeal, Nucor acknowledges that it had
the burden of proving a deficiency had occurred in the Final Permit or in the permitting
process. However, Nucor contends that the AHO erred in requiring it to prove not only
that a deficiency occurred but that the deficiency was so material that it would have caused
an exceedance of air-quality standards.
We note at the outset that Nucor does not discuss any specific instances in which the
AHO imposed an enhanced burden of proof. Moreover, Nucor cites no authority and
makes no convincing argument for the proposition that PC&E lacks the authority to
determine whether an error is so immaterial that reversal is not required. It is Nucor’s burden
to demonstrate reversible error, Stevens v. SEECO, Inc., 2015 Ark. App. 322, and we will
not develop an appellant’s argument on appeal. Orintas v. Point Lookout Prop. Owners Ass’n,
2015 Ark. App. 648. We therefore affirm on this point.
Nucor also claims that the AHO rendered his decision based on an “improper
separation” of the issues. According to Nucor, the AHO ruled that certain, individual
deficiencies in the permit process had a negligible effect on air-quality standards but failed
to consider the cumulative impact of all deficiencies. While the AHO did, in some instances,
cite the de minimis effect of an alleged deficiency, it was generally done as an alternative
reason for rejecting Nucor’s arguments. We therefore see no reversible error. Moreover, as
will be seen in our upcoming discussion of the issues, only one point will be affirmed based
on the negligible effect of any possible error.
Lastly, we address Nucor’s argument that the AHO improperly dismissed some of
the paragraphs in its petition for review on procedural grounds. The AHO found that some
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of Nucor’s allegations were barred by not having been raised in the public comments. See
Ark. Code Ann. § 8-4-205(b)(2) (providing that a third party cannot raise an issue in a
PC&E hearing if the issue was not first raised in the public comments, unless he can show
good cause why he could not, with reasonable diligence, have discovered and presented the
issue during the comment period). Others were dismissed for being too general in nature,
see Ark. Code Ann. § 8-4-205(b)(3) (providing that a request for a PC&E hearing must
include a complete and detailed statement identifying the legal and factual objections to
the permit), or for incorporating allegations from other sources. See Ark. PC&E Reg.
8.603(c)(1)(c).
On appeal, Nucor argues that the procedural dismissals were based on a hyper-
technical application of the above-mentioned statutes and regulations. However, Nucor’s
brief does little more than set forth a list of paragraph numbers that were dismissed; it
provides no explanation as to why the dismissals warrant reversal. As stated above, it is
Nucor’s burden to demonstrate reversible error, Stevens, supra, and we will not develop an
appellant’s argument on appeal. Orintas, supra.
Nucor also contends that the AHO improperly excluded certain witness testimony
as it pertained to the dismissed paragraphs. However, Nucor does not proffer the substance
of the testimony or explain how it was prejudiced by the testimony’s exclusion. See Turner
v. N.W. Ark. Neurosurgery Clinic, 84 Ark. App. 93, 133 S.W.3d 417 (2003) (holding that we
will not reverse the exclusion of evidence in the absence of a demonstration of prejudice).
Consequently, we affirm the dismissals and the exclusion of evidence.
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VI. Alleged Misrepresentation
During the permit-application process, BRS provided ADEQ with certain “emission
factors,” which estimated the quantity of a particular pollutant that would be emitted from
each particular emission source. For example, with regard to emissions from the plant’s
natural-gas-fired equipment, BRS submitted a PM2.5 emission factor of .00052 pounds per
one million BTUs (.00052 lb./MMBTU). According to BRS consultant Steven Frey, BRS
did not submit any emission factor to ADEQ unless the manufacturer of the natural-gas-
fired equipment—SMS Siemag (SMS)—confirmed that the factor could be achieved.
ADEQ, in turn, relied on BRS’s representation that the emission factors were achievable.
Consequently, ADEQ accepted the factors and used them in the Draft Permit as the PM2.5
emission limits for the steel mill’s natural-gas-fired sources.
After the Draft Permit was issued, and during the thirty-day public-comment period,
SMS sent emails to BRS stating that it was “unknown if such low [emission] values can be
achieved at all by the affected units,” and that “we cannot guarantee that the required PM
figures can be achieved.” BRS did not notify ADEQ that SMS had expressed doubts about
the achievability of the emission limits.
When the Final Permit was issued, Nucor appealed to PC&E. The parties then
conducted discovery, and Nucor obtained the SMS emails as part of over 90,000 pages
provided by BRS. During the adjudicatory hearing, Nucor admitted the emails into
evidence through BRS’s expert Gale Hoffnagle. Mr. Hoffnagle said he had never seen the
emails but that it would be important for regulators to know the achievability of emission
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factors. He also testified that he believed BRS’s stated emission limits could be met and that,
at some point after the emails were sent, the engineers must have confirmed achievability.
Following the hearing, Nucor asked PC&E to make a finding that BRS’s permit
should be revoked based on BRS’s failure to disclose SMS’s concerns about the emission
limits. The AHO declined to do so, ruling that “even if a misrepresentation occurred in this
case” PC&E was not authorized to revoke BRS’s permit. As authority for this ruling, the
AHO cited Arkansas Code Annotated section 8-4-204 (Repl. 2011), which provides that
ADEQ has the power to revoke, modify, or suspend a permit on the ground of
misrepresentation. (Emphasis added.) Nucor urged PC&E’s Commissioners to reject the
AHO’s ruling, arguing that the AHO had abdicated his duty to revoke the permit. PC&E
instead affirmed. 4
On appeal to this court, Nucor seeks reversal of PC&E’s decision on the ground that
BRS concealed material information from ADEQ during the application process and from
the public during the comment period. However, PC&E made no finding as to whether a
misrepresentation occurred. It ruled only that it lacked the legal authority to revoke BRS’s
permit.
A finding or conclusion by a lower tribunal, if not attacked on appeal, must stand as
a basis for affirmance. See generally Sheppard v. Ark. Alcoholic Bev. Control Bd., 2014 Ark. App.
604, 447 S.W.2d 614; Camp v. State, 66 Ark. App. 134, 991 S.W.2d 611 (1999). In its
4
Around this time, Nucor sent correspondence to ADEQ Director Teresa Marks
demanding that ADEQ revoke, suspend, or modify BRS’s permit. When Marks did not
respond, Nucor sought a writ of mandamus in Pulaski County Circuit Court. The court
refused to grant the writ, noting that the AHO had not found that a misrepresentation
occurred and that the Director’s decision on the matter was discretionary.
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opening brief, Nucor addresses the alleged misrepresentation but fails to challenge the
AHO’s finding that PC&E was not authorized to revoke BRS’s permit. Nucor’s opening
brief contains no argument that PC&E erred in finding that it lacked authority to revoke
the permit. The only sentence in Nucor’s opening brief that might be interpreted as raising
this issue states as follows:
It was also an abuse of discretion for PC&E not to initiate its own investigation
or to remand the matter to ADEQ to determine precisely who knew what
and when about this matter and to take such further action as is required by
law upon determining the full extent of the concealment and cover-up.
This sentence appears at the end of Nucor’s substantive argument on the misrepresentation
issue and is simply a conclusory statement on its position that there was misrepresentation
in the permitting process. It does not refer to, or in any way challenge, the AHO’s lack-
of-authority finding. At oral argument, Nucor’s counsel was asked to point out where in its
opening brief Nucor argued that the AHO’s lack-of-authority finding was error. He
responded by stating that he would provide that information to the court after the
arguments, and he filed a letter to the court later that day. But counsel misapprehends the
issue, demonstrating only that Nucor preserved a separate argument regarding the standard
of review.
Thus, Nucor failed to attack the only finding the AHO made on the issue, i.e., that it
lacked authority to revoke the permit. Consequently, we affirm this point without reaching
the underlying misrepresentation allegations. Sheppard, supra; Camp, supra. Moreover, an
appellant must cite authority and demonstrate error by making a convincing argument as to
why the tribunal erred and why reversal is required. See Orintas, supra; Parker v. Parker, 97
Ark. App. 298, 248 S.W.3d 523 (2007). Because Nucor failed to make any argument for
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reversal as to the AHO’s lack-of-authority finding, it clearly has not carried its burden of
presenting convincing argument and authority supporting its position. 5 We therefore affirm
on this point.
VII. Air-Quality Analysis
We now turn to Nucor’s many arguments pertaining to the air-quality analysis and
the modeling that BRS performed in connection with its PSD application. We first address
Nucor’s claim that BRS’s analysis incorrectly employed Significant Impact Levels (SILs).
SILs are screening methods adopted by the EPA in an effort to exempt an applicant
from conducting a full analysis of certain pollutants when the predicted levels of those
pollutants are below certain concentrations. In January 2013, while BRS’s application was
pending, a federal circuit court vacated some portions of the EPA’s SIL regulations. See
Sierra Club v. Env. Prot. Agency, 705 F.3d 458 (D.C. Cir. 2013). Nucor contends that, in
light of the Sierra Club holding, BRS incorrectly employed SILs in its air-quality analysis
(although PM2.5 did receive a full analysis).
The AHO dismissed this argument on the ground that it was procedurally barred by
not having been raised in the public comments as required by Arkansas Code Annotated
section 8-4-205(b)(2). We affirm that ruling. Nucor’s Comment 30, on which it relies,
challenged BRS’s usage and placement of receptors in its significance modeling. However,
the comment does not raise the issue that the SILs have been vacated and are no longer
applicable.
Nucor argued in its reply brief that the lack-of-authority finding was erroneous,
5
but we have previously held that an argument developed for the first time in a reply brief
comes too late. Orintas, supra.
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Nucor also argues that BRS’s air-quality analysis was flawed because it did not
consider “secondary” PM2.5 formation. By way of explanation, PM2.5 may be emitted
directly from a mill’s emission sources, or it may develop secondarily in the atmosphere
through chemical reaction of certain precursors, such as nitrogen oxides and sulfur dioxide,
which are also emitted from the mill. The AHO ruled that BRS had no legal obligation to
account for secondary PM2.5 in its air-quality modeling.
Since the onset of its regulation of PM2.5 in 1997, the EPA has struggled with the
issue of secondary formation. According to Nucor, a 2008 EPA rule required a PSD
applicant to model secondary formation, which would naturally lead to an increase in PM2.5
concentration. However, the requirements of the 2008 rule are not clear, and BRS expert
Gale Hoffnagle testified that there was no legal authority that required such modeling.
Indeed, subsequent EPA documents indicate that unresolved issues have remained as to
whether secondary formation must be modeled and, if so, by what method. In March 2013,
the EPA issued a draft guidance memorandum in which it noted that its preferred air-quality
model, AERMOD, did not account for secondary formation. The draft therefore included
recommended approaches for assessing the impact of secondary formation. However, an
accompanying letter stated that the draft was a statement of preliminary recommendations;
that it was not yet considered final guidance; and that it contained no binding, enforceable
requirements.
At the adjudicatory hearing, Nucor’s experts testified that modeling of secondary
PM2.5 was required and that ADEQ should have followed the EPA’s draft guidance and
insisted on such modeling before issuing the BRS permit. However, ADEQ Director Teresa
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Marks testified that ADEQ considered the EPA guidance to be nonbinding. Still, ADEQ
engineers were concerned enough to email the EPA and ask how to approach the issue of
secondary formation. The EPA did not respond. Later, after the Draft Permit was issued,
the EPA made thirteen comments regarding changes that should be made in the permit.
None involved secondary formation of PM2.5.
Based on the foregoing, and giving due regard to the administrative agency’s
expertise, we see no abuse of discretion or error of law on this point. It is unclear whether
any authority required the modeling of secondary PM2.5, and we will not reverse an agency’s
interpretation of statutes and regulations unless the interpretation is clearly wrong. Lamar
Outdoor Advert., supra. Further, there was substantial evidence that ADEQ was not required
to follow the EPA guidance on an issue, much less draft guidance. We therefore reject
Nucor’s argument.
Next, Nucor challenges BRS’s decision to use Dyersburg, Tennessee, as a
representative location for monitoring background PM2.5. The Clean Air Act generally
requires pre-construction air-quality monitoring for a period of one year preceding the
permit application. 42 U.S.C. § 7475(e)(2); 40 C.F.R. 52.21(m)(1)(iv). However, if there
are no monitors located in the vicinity of the proposed construction that can be used to
obtain the necessary background concentrations, a regional site may be used. 40 C.F.R. Part
51, Appx. W at 8.2.2(c). A regional site is one that is located away from the area of interest
but is impacted by similar natural and distant man-made sources. Id.
Here, Mississippi County had no monitor to measure background PM2.5. BRS
therefore used the monitor at Dyersburg, and ADEQ accepted Dyersburg as a representative
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location. Nucor’s experts criticized the use of Dyersburg and proposed the use of a monitor
located in Marion, Arkansas. However, BRS and ADEQ witnesses testified that Dyersburg
was similar to Mississippi County in land use, population, and terrain, and was therefore a
proper representative monitoring site. PC&E credited the testimony of BRS and ADEQ
witnesses, as was its prerogative. Williams v. Ark. State Bd. of Physical Therapy, 353 Ark. 778,
120 S.W.3d 581 (2003). We therefore affirm on this point.
Nucor further contends that BRS failed to model all of the steel mill’s emission
sources. According to BRS’s permit application, the proposed mill contained approximately
100 sources of pollutant emissions, including sixteen sources from the mill’s melt shop. It is
undisputed that BRS neglected to model the sixteen melt-shop sources. One of Nucor’s
experts, Mr. Schewe, testified that he ran a model that included all omitted sources and that
the result showed an exceedance of the PM2.5 air-quality standards. However, BRS’s expert,
Mr. Hoffnagle, calculated that the omitted sources would only have increased the PM2.5
concentration level by .004 µg/m3, meaning that no exceedance of air-quality standards
would have occurred. PC&E accepted Mr. Hoffnagle’s analysis, and we defer to the agency’s
expertise on this matter. The credibility and the weight of the evidence is within the
administrative agency’s discretion. Williams, supra.
We next address Nucor’s claim that BRS’s air-quality analysis did not properly
consider a phenomenon known as “building downwash.” Downwash occurs when
turbulence forms as air tries to pass around a building. When an emission source is located
close enough to the turbulence, the emitted exhaust plume may be mixed closer to
the ground, resulting in a higher pollutant concentration. BRS’s modeling correctly
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incorporated the downwash characteristics of its own buildings. Yet Nucor contends that
the downwash characteristics of other, nearby industries, such as the Bunge Grain Elevator,
should also have been incorporated into the modeling. PC&E ruled that it knew of no legal
authority for the proposition that BRS was required to consider downwash from other
facilities. Given that Nucor has not demonstrated that PC&E erred in this conclusion, we
see no basis for reversal.
The Bunge Grain Elevator also figures in the final point under this topic. As
mentioned earlier, BRS’s initial modeling runs predicted that its mill, along with nearby
industries would generate a PM2.5 concentration level of 2.56 µg/m3. Upon receiving these
results and discussing the matter with ADEQ, BRS consultant Steven Frey reassessed his
modeling. One of the inputs he had used in his modeling was the PM2.5 emission level
generated by the Bunge facility. The original inputs for Bunge used data derived from a
twenty-four-hour-per-day operation. Frey determined that Bunge did not operate twenty-
four hours per day, and therefore the PM2.5 emissions from Bunge were overestimated. Frey
then reduced the Bunge emission data to represent a twelve-hour-per-day operation. By
using this new data, BRS’s subsequent PM2.5 modeling calculation was reduced to 2.47
µg/m3. PC&E ruled that the adjustment was acceptable because it was more representative
of the actual operating hours of the grain elevator.
Nucor contends that BRS did not follow the EPA modeling guidance in making the
Bunge adjustment. It cites a footnote to a table in 40 C.F.R. Part 51, Appendix W, as
authority that BRS’s model was required to use an actual, two-year average for Bunge’s
operating hours. However, that regulation also allows for the exercise of professional
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judgment by the permitting authority in the modeling of nearby facilities. Given the
testimony that the adjustment was more reflective of Bunge’s actual operation, and that
BRS sought ADEQ approval before making the adjustment, we decline to reverse in light
of our limited review.
VIII. Errors Affecting Public Comment
State regulators must provide an opportunity for public comment on the information
submitted by the applicant for a new-construction permit. 40 C.F.R. §§ 51.161(b)(2) &
51.166(q)(2)(ii). Accordingly, PC&E regulations state that no permit shall be issued unless
the public has first had the opportunity to comment on the information submitted by the
applicant and on ADEQ’s analysis of the effect of the new construction on the region’s air
quality. Ark. PC&E Regs. 18.306(A) & 19.406(A). In addition, ADEQ must submit a
Statement of Basis setting forth the legal and factual basis for the Draft Permit. Ark. PC&E
Reg. 26.506. Nucor argues that, for several reasons, the public in this case was denied the
chance for meaningful and informed comment on BRS’s application and on the Draft
Permit.
We first dispose of Nucor’s arguments that public comment was thwarted by the
alleged misrepresentations of emission achievability; the failure to model secondary PM2.5;
the use of SILs; and the Bunge Grain Elevator adjustment. In light of our earlier holdings
that no reversible error was demonstrated with regard to these very matters, there is likewise
no basis for reversal under this heading.
For its remaining arguments, Nucor first contends that ADEQ made improper
changes in the Draft Permit regarding certain Nitrogen Oxide values. We disagree. The
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Draft Permit originally showed that BRS demonstrated a one-hour Nitrogen Oxide value
of 37.6 µg/m3. During the comment period, BRS stated that this figure was erroneous and
should have been 181.8 µg/m3, which was still below the federal ceiling of 188. ADEQ
made the change, and the Final Permit reflected the 181.8 figure. Clearly, ADEQ made an
open and above-board correction of what appears to be a mere scrivener’s error. We
therefore see no reason to hold that the correction adversely affected the public’s ability to
comment.
Secondly, Nucor cites a change made in the Final Permit regarding BRS’s
Greenhouse Gas (GHG) emissions. BRS’s final application proposed a limit of .0723 tons
of GHG per ton of liquid steel produced per year for certain operations. ADEQ placed this
limit in the Draft Permit. However, after the Draft Permit was issued, BRS made a comment
seeking a higher limit. BRS stated that the limit in the Draft Permit was based on an
anticipated product mix, which, if changed, could produce higher emissions. BRS therefore
asked ADEQ to increase the limit to .155 tons of GHG per ton of liquid steel to reflect a
“worst case production output.” The Final Permit contained the revised limit.
Without belaboring the point, we agree with PC&E that Nucor has not shown that
a change in a Draft Permit, made by ADEQ in response to a public comment, requires the
public-comment period to begin anew. Nucor’s expert, Dr. Zeng, acknowledged that
ADEQ incorporates changes into the Final Permit, based on public comments, and that the
changes do not necessarily “have to go back out” for public comment. We affirm on this
point.
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IX. Other Allegations of Error
Nucor claims that BRS and ADEQ used improper emission factors to estimate the
emissions that would be discharged from certain plant sources. The EPA has a clearinghouse
designated as AP-42, on which air-quality modelers may draw to obtain standardized
emission factors. In this case, BRS and ADEQ did not use AP-42 but instead used factors
developed by the Minnesota Pollution Control Agency. The Minnesota factors were much
lower, and Nucor’s experts testified that they were unreliable and unachievable. However,
BRS and ADEQ witnesses stated that the Minnesota figures were reliable and were actually
developed by EPA. PC&E credited BRS’s and ADEQ’s testimony, and we defer to the
agency’s decision on the credibility of witnesses and weight to be given their testimony.
Williams, supra.
Nucor also argues that the emission rates from “several natural-gas combustion
sources” were increased in the Final Permit but were not remodeled. However, Nucor’s
brief does not identify these sources or otherwise provide us with sufficient information to
conduct a review of this point. We therefore will not reverse. See Orintas, supra.
Finally, Nucor argues that BRS and ADEQ failed to conduct an appropriate
additional-impact analysis. As part of the PSD process, an applicant must conduct an analysis
of any impairment that its facility will cause to soil and vegetation and to visibility. The
applicant must also assess the air-quality impact as a result of general commercial, residential,
industrial, and other growth associated with the new plant. 40 C.F.R. 52.21(o). BRS’s
growth analysis reads as follows:
The project being proposed by BRS will have no effect on construction and growth
impacts. During the construction phase, BRS will employ various techniques to
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minimize the potential impact on the surrounding environment. The primary focus
will be to reduce the formation of fugitive type particulates that may be generated
during the construction phase.
The construction and operation of the proposed steel plant should not result in any
noticeable residential growth in the area. Commercial growth is anticipated to occur
at a gradual rate in the future. However, this growth will not be directly associated
with the proposed plant in Mississippi County. The proposed plant should have a
positive impact on the economic climate of Osceola by providing jobs for the area
workforce.
Nucor’s expert, Mr. Schewe, offered his opinion that the above analysis should have
been more “robust.” However, PC&E discounted that opinion because Schewe had no
expertise in economic-growth analysis and did not conduct an economic analysis of the
Mississippi County area. Further, ADEQ witness Thomas Rheaume testified that there were
no legal guidelines for performing an additional-impact growth analysis and that the analysis
submitted by BRS was consistent with the level of detail in past analyses received by ADEQ.
Thus, as with other issues in this case, we recognize the specialization and experience of
PC&E on these matters and, due to our limited review, affirm PC&E’s ruling.
Affirmed.
ABRAMSON and VAUGHT, JJ., agree.
Dover Dixon Horne PLLC, by: Mark H. Allison; and Bradley Murchison Kelly & Shea
LLC, by: David R. Taggart, Pro Hac Vice, for appellants.
Leslie Rutledge, Att’y Gen., by: Jamie Ewing, Ass’t Att’y Gen., for appellee Arkansas
Pollution Control and Ecology Commission.
Baker Hostetler LLP, by: Martin T. Booher and Michael Montgomery; and Mitchell
Williams PLLC, by: Adria W. Conklin, for appellee Big River Steel LLC.
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