# Sound Rivers

> Court of Appeals of North Carolina · June 2, 2020

URL: https://www.frixlaw.com/law-library/cases/10485872

## Case

- **Court:** Court of Appeals of North Carolina
- **Decided:** June 2, 2020
- **Precedential status:** Published
- **Opinion:** Opinion
- **Cited by:** 0 later opinions in the Frix Law Library

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## Opinion text

IN THE COURT OF APPEALS OF NORTH CAROLINA

No. COA18-712

Filed: 2 June 2020

Beaufort County, No. 15 CVS 262

Carteret County, No. 16 CVS 1272

SOUND RIVERS, INC. and NORTH CAROLINA COASTAL FEDERATION, INC.,
Petitioners,

v.

N.C. DEPARTMENT OF ENVIRONMENTAL QUALITY, DIVISION OF WATER
RESOURCES, Respondent, MARTIN MARIETTA MATERIALS, INC., Respondent-
Intervenor.

Appeal by respondent North Carolina Department of Environmental Quality,

Division of Water Resources, respondent-intervenor Martin Marietta Materials, Inc.,

and cross-appeal by petitioners Sound Rivers, Inc. and North Carolina Coastal

Federation, Inc., from orders entered 13 November 2015 by Judge W. Douglas

Parsons in Superior Court, Beaufort County, 30 October 2017, 4 December 2017, and

20 December 2017 by Judge Joshua W. Willey, Jr in Superior Court, Carteret County.

Heard in the Court of Appeals 22 May 2019.

Southern Environmental Law Center, by Geoffrey R. Gisler, Blakely E.
Hildebrand, and Jean Zhuang, for petitioner-appellees.

Attorney General Joshua H. Stein, by Assistant Attorney General Asher P.
Spiller and Assistant Attorney General Scott A. Conklin, for respondent-
appellant.

Brooks, Pierce, McLendon, Humphrey & Leonard, L.L.P., by Matthew B.
Tynan, George W. House, Alexander Elkan and V. Randall Tinsley, for
respondent-intervenor-appellant.
SOUND RIVERS, INC. V. NC DEP’T OF ENVTL. QUALITY

Opinion of the Court

STROUD, Judge.

This case arises from the issuance of a National Pollutant Discharge

Elimination System Permit (“Permit”) by respondent North Carolina Department of

Environmental Quality, Division of Water Resources (“DEQ”) to respondent-

intervenor Martin Marietta Materials, Inc., (“Martin Marietta”) allowing respondent

Martin Marietta to discharge wastewater from Vanceboro Quarry (“quarry”) into

“unnamed tributaries to Blounts Creek[.]” The Administrative Law Judge (“ALJ”) of

the Office of Administrative Hearings (“OAH”) entered a final decision affirming the

issuance of the Permit. Petitioners Sound Rivers, Inc. and North Carolina Coastal

Federation, Inc. (“Petitioners”) filed a petition for judicial review with the superior

court.1 The superior court reversed the ALJ’s final decision based upon a failure to

“ensure reasonable compliance with the biological integrity standard” (“biological

integrity standard”) found in the North Carolina Administrative Code (“Code”) but

concluded that the Permit was in compliance with other water quality standards,

including “swamp waters supplemental classification and the state antidegradation

rule” (“swamp waters”) and pH (“pH standards”).

1 Petitioner Sound Rivers, Inc. was known as the Pamlico-Tar River Foundation when the original

petition for a contested case hearing was filed; it noted its name had changed to Sound Rivers, Inc.
effective 1 April 2015 in its 20 April 2015 petition for judicial review. For simplicity, we will refer to
the petitioner throughout this opinion as Sound Rivers.

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Opinion of the Court

Respondent Martin Marietta and respondent DEQ appeal from the superior

court’s order reversing the ALJ’s order due to its conclusion on biological integrity

standards. Petitioners cross-appeal from the superior court’s order based upon its

conclusion that the Permit reasonably ensured compliance with water quality

standards regarding swamp waters and pH standards. We note at the outset that at

all stages of the proceedings, the parties have filed numerous documents, including

briefs, motions, proposed drafts of orders, responses, and exhibits; in this opinion we

will mention only those documents relevant to the issue on appeal as the documents

are so voluminous, but we have reviewed all of the documents before us and after

review of the briefs, record, and transcripts, we affirm the superior court’s order as to

swamp waters and pH standards and reverse as to the biological integrity standard.

I. Factual and Procedural Background

In September of 2013, Sound Rivers and North Carolina Coastal Federation

filed a petition for a contested case hearing on DEQ’s issuance of the Permit on 24

July 2013 to Martin Marietta. According to the petition, the Permit authorized

Martin Marietta to “the discharge of 12 million gallons of mine wastewater into

tributaries of Blounts Creek each day.” Petitioners alleged the Permit violated

“applicable laws” attached and incorporated into the petition.

The Permit was issued under the provisions of North Carolina General Statute

§ 143-215.1 and “other lawful standards and regulations promulgated and adopted

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Opinion of the Court

by the North Carolina Environmental Management Commission, and the Federal

Water Pollution Control Act, as amended[.]” The Permit was effective on 1 September

2013 and would expire on 31 August 2018.2 The Permit allowed Martin Marietta to

discharge water pumped from its quarry “from two pit clarification ponds” identified

on an attached map into “receiving waters designated as unnamed tributaries to

Blounts Creek in the Tar-Pamlico River Basin in accordance with effluent limitations,

monitoring requirements, and other conditions set forth in Parts I, II, and III” of the

Permit. The supplement to the Permit cover sheet noted that the “unnamed

tributary” into which the wastewater would be discharged was “classified as C-

Swamp NSW waters in the Tar-Pamlico River Basin.” In this opinion, we will refer

to the waters into which wastewater from the quarry would be discharged as “Blounts

Creek.”

In September of 2013, respondent DEQ submitted a prehearing statement

identifying the issues to be resolved as

2 No party has argued this case may be moot based upon the fact that the Permit as issued would have

expired in 2018. “A case is ‘moot’ when a determination is sought on a matter which, when rendered,
cannot have any practical effect on the existing controversy. Thus, the case at bar is moot if an
intervening event had the effect of leaving plaintiff with no available remedy. A moot claim is not
justiciable, and a trial court does not have subject matter jurisdiction over a non-justiciable claim.
Moreover, if the issues before the court become moot at any time during the course of the proceedings,
the usual response is to dismiss the action for lack of subject matter jurisdiction.” Cumberland Cnty.
Hosp. Sys., Inc. v. N.C. Dep’t of Health & Human Servs., 242 N.C. App. 524, 528-29, 776 S.E.2d 329,
333 (2015) (citations, quotation marks, brackets omitted). But an exception to the mootness doctrine
applies to this case because it is “capable of repetition, yet evading review[.]” Id. at 529, 776 S.E.2d at
333-34 (“Two elements are required for the capable of repetition, yet evading review exception to apply:
(1) the challenged action is in its duration too short to be fully litigated prior to its cessation or
expiration, and (2) there is a reasonable expectation that the same complaining party would be
subjected to the same action again.” (citations, quotation marks, and brackets omitted)).

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Opinion of the Court

[(1)] whether Respondent, properly issued the Permit
pursuant to Article 21, Chapter 143 of the North Carolina
General Statutes and the applicable rules promulgated
thereunder, including but not limited to 15A NCAC
2B.0200 et. seq.; and [(2)] whether Respondent, in issuing
the Permit substantially prejudiced Petitioner’s rights and
erred in one or more of the five ways enumerated in N.C.
Gen. Stat. § 150B-23(a).

Martin Marietta, who had intervened, also submitted a prehearing statement

contending the Permit “would not violate water quality standards” and noted that

the Permit had been issued “after years of pre-permitting work, the submission of

engineering, economic, and ecological studies and materials by Martin Marietta, and

extensive review and analysis by DWR [, Division of Water Resources,] and other

state and federal government agencies.” Martin Marietta contended state and federal

regulatory personnel had thoroughly analyzed the proposed permit over about

eighteen months, including “site visits, field work, numerous communications and

meetings, the further submission of materials and studies by Martin Marietta, and

public comment and a public hearing, in which Petitioners and their members and

counsel participated.” Thus, Martin Marietta contended state and federal regulatory

personnel had already considered the “claims asserted by Petitioners in this contested

case” and DEQ “correctly concluded that the proposed discharge allowed by the NPDS

Permit would not violate water quality standards and lawfully and appropriately

issued the NPDES Permit.”

On 6 November 2013, Petitioners filed their prehearing statement contending

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Opinion of the Court

that the Permit did not comply with biological integrity standards, protection of

swamp waters, and pH standards, and identifying the issues as:

1. The Clean Water Act and state laws implementing
it prohibit discharges that violate any water quality
standard. State water quality standards for waters
like Blounts Creek prohibit any discharge that will
make a waterbody unsuitable for native plants and
animals, violating its “biological integrity.” Martin
Marietta’s proposed discharge of 12 million gallons
of mine wastewater per day into Blounts Creek
would displace native fish, macroinvertebrates
(insects, mollusks, crayfish, etc.) and plants. Did
DWR exceed its authority, act erroneously, fail to
use proper procedure, act arbitrarily or capriciously
or fail to act as required by rule or law “err”) by
authorizing the discharge?

2. The Clean Water Act and state laws implementing
it prohibit discharges that violate any water quality
standard. The state water quality standard for pH
is the normal pH for the waterbody receiving a
discharge, which is between 4.0 and 5.5 in Blounts
Creek. Did DWR err by authorizing a discharge that
would raise the pH in the creek to a minimum of 6.3
to 6.9?

3. The Clean Water Act and state laws implementing
it require classification of waters to protect existing
uses. North Carolina has classified Blounts Creek
as swamp waters to protect characteristics unique to
these waters, including low flow and velocity, low
pH, and high tannin levels. Did DWR err by issuing
a permit for a discharge that will cause Blounts
Creek to have higher flow and velocity, near neutral
pH, and low tannin levels, thereby no longer
qualifying as swamp waters?

In November of 2014 Petitioners filed a motion for summary judgment on the

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Opinion of the Court

issues of whether Petitioners were “persons aggrieved” under North Carolina’s

Administrative Procedure Act and whether DWR had exceeded its authority or failed

to act as required by law based upon failure to ensure compliance with the biological

integrity water quality standard, the pH water quality standard, and Blounts Creek’s

swamp waters classification. Petitioners also submitted numerous affidavits to

support their motion. On 25 November 2014, Martin Marietta filed a motion for

summary judgment.

On 23 March 2015, the ALJ entered an order granting summary judgment for

respondents. The order stated at length the undisputed facts and concluded

“Petitioners are not ‘Persons Aggrieved[;]’” “Respondent’s Decision to Issue the

Permit was Not in Violation of N.C. Gen. Stat. § 150B-23(a)[;]” “Respondent Ensured

Compliance with Biological Integrity Standard[;]” “Respondent Ensured Compliance

with pH Water Quality Standards[;]” and “Respondent Protected Existing Uses[.]”

The ALJ also noted the “Re-opener Provision” of the Permit:

The permit issued to the Respondent-Intervenor
allows the Respondent to re-open and modify the permit if
water quality standards are threatened or other monitored
data cause concern. Even if Petitioner provided evidence
of specific and particularized potential violations of water
quality standards, the re-opener provision assures
reasonable compliance with those standards.

In summary, the ALJ concluded,

There is no evidence that Petitioners’ rights have
been substantially prejudiced, or that Respondent

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Opinion of the Court

exceeded its authority or jurisdiction, acted erroneously,
failed to use proper procedure, acted arbitrarily or
capriciously, or failed to act as required by law or rule.

For the reasons discussed herein, there is no genuine
issue as to any material fact. Respondent’s Motion for
Summary Judgment is allowed; Respondent-Intervenor’s
Motion for Summary Judgment is allowed. Petitioners’
Motion for Summary Judgment is denied, and Petitioners
are not entitled to the relief requested in the petition.

On 20 April 2015, Petitioners filed a petition for judicial review of the summary

judgment order contesting the ALJ’s determinations. On 20 May 2015, Martin

Marietta responded to and filed a motion to dismiss petitioners’ petition for judicial

review, arguing the superior court did not have subject matter jurisdiction because

petitioners are not “persons aggrieved” and therefore not entitled to judicial review.

On 13 November 2015, the superior court entered its order denying Martin Marietta’s

motion to dismiss and denying petitioner’s petition on all grounds except for the issue

of “persons aggrieved.” The superior court concluded petitioners were persons

aggrieved and remanded the matter back to OAH for a “full plenary hearing[.]”

After a “hearing on the merits May 31, 2016 through June 9, 2016[,]” on 30

November 2016, the ALJ issued a 62-page final decision. The final decision addressed

four primary issues:

Issue 1: “pH Claim”: Whether Petitioners have met their
burden of proving that Respondent exceeded its authority
or jurisdiction, acted erroneously, failed to use proper
procedure, acted arbitrarily or capriciously, or failed to act
as required by law or rule in determining the NPDES

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Opinion of the Court

Permit reasonably ensures compliance with the pH water
quality standard.

Issue 2: “Swamp Waters Claim”: Whether Petitioners
have met their burden of proving that Respondent
exceeded its authority or jurisdiction, acted erroneously,
failed to use proper procedure, acted arbitrarily or
capriciously, or failed to act as required by law or rule in
determining the NPDES Permit reasonably ensures
compliance with water quality standards and regulations
related to the “Swamp Waters” supplemental
classification.

Issue 3: “Biological Integrity Claim”: Whether
Petitioners have met their burden proving that Respondent
exceeded its authority or jurisdiction, acted erroneously,
failed to use proper procedure, acted arbitrarily or
capriciously, or failed to act as required by law or rule in
determining the NPDES Permit reasonably ensures
compliance with the biological integrity water quality
standard.

Issue 4: Substantial Prejudice: Whether Petitioners
have met have their burden of proving that Respondent
substantially prejudiced Petitioners’ rights in issuing the
NPDES Permit.

The ALJ made 311 findings of fact; we will address some of these findings of

fact below in detail in our discussion of the challenged findings applicable to each

issue. The order ultimately denied Petitioners’ claims based upon two alternative

and independent grounds: First, “Petitioners failed to meet their burden of proving

by a preponderance of evidence that Respondent DWR exceeded its authority or

jurisdiction, acted erroneously, acted arbitrarily and capriciously, used improper

procedure, or failed to act as required by law or rule in issuing the NPDES Permit.”

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Opinion of the Court

Second, as an independent and alternative basis for the ruling, “Petitioners failed to

carry their burden of proof by a preponderance of the evidence that their rights have

been substantially prejudiced by Respondent DWR’s issuance of the NPDES Permit.”

In December of 2016, Petitioners filed a petition in superior court for judicial

review of the ALJ’s final decision. Petitioners alleged the order was in error in that

“The Final Decision Contains Findings of Fact Unsupported by Substantial Evidence,

Findings That Are Arbitrary, Capricious, or an Abuse Of Discretion, and Findings

Affected By Other Errors Of Law[;]” “The ALJ’s Conclusion That Petitioners Are Not

Substantially Prejudiced Is Erroneous[;]” “The ALJ’s Grant of Deference to DWR

Staff And [Martin Marietta] Consultants Is An Error Of Law[;]” “The ALJ’s

Conclusion That DWR Complied with the Biological Integrity Standard Is

Erroneous[;]” “The ALJ’s Conclusion That DWR Complied with the pH Standard Is

Erroneous[;]” “The ALJ’s Conclusions of Law Regarding the Swamp Waters

Classification And Antidegradation Rules Are Erroneous[;]” and “The ALJ’s

Conclusion That the Required Reopener Provision Ensures Compliance With Water

Quality Standards Is Erroneous[.]”

On 30 January 2017, Martin Marietta filed a motion to dismiss the petition

under North Carolina General Statute § 150B-46 and North Carolina Rule of Civil

Procedure 12 because the petition for judicial review was not timely served. On 30

October 2017, the superior court denied Martin Marietta’s motion to dismiss. On 4

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December 2017, the superior court denied Martin Marietta’s motion to dismiss for

failure to state a claim under North Carolina Rule of Civil Procedure 12(b)(6).

On 20 December 2017, the superior court entered its order on petition for

judicial review. The superior court noted these issues:

I. Did the ALJ err in admitting, considering, or
determining the credibility or weight of evidence?

II. Did the ALJ err in upholding DWR’s issuance of the
Permit as reasonably ensuring compliance with:
A. The swamp waters supplemental
classification and antidegradation rule;
B. The water quality standard for pH; and
C. The water quality standard for biological
integrity?

III. Did the ALJ err in holding that the Permit’s
monitoring and reopener provisions further
reasonably ensure compliance with state water
quality standards?

IV. Did the ALJ err in holding that Petitioners failed to
prove their rights were substantially prejudiced?

The superior court entered its order in paragraph form with no numbered findings of

fact and with two conclusions of law. Ultimately, the superior court concluded

Petitioners were “substantially prejudiced by the issuance of the Permit and are

entitled to the relief sought.” On the substantive issues regarding water quality

standards, the superior court concluded that DEQ “did not ensure reasonable

compliance with the biological integrity standard as set forth in 15A N.C.A.C. 02B

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Opinion of the Court

.211(2), 0220(2), and 0202(11)” and therefore reversed the final decision of the ALJ

and vacated the Permit.

Over the course of 10 days, all parties filed written notices of appeal and cross-

appeal, seeking review of the following orders:

1. 13 November 2015 order granting summary judgment to Petitioners regarding
being “persons aggrieved” and denying all other matters;

2. 27 February 2017 ruling from the superior court denying Martin Marietta’s
motion to dismiss and granting Petitioners’ motion for extension of time;

3. 30 October 2017 order memorializing 27 February 2017 ruling that denied
Martin Marietta’s motion to dismiss and granted Petitioners’ motion for
extension of time;

4. 4 December 2017 order denying Martin Marietta’s motion to dismiss, and

5. 20 December 2017 superior court order on the petition for judicial review
vacating the Permit.

II. Preliminary Issues

We begin our analysis by addressing preliminary issues.

A. Martin Marietta’s Motion to Dismiss

On 30 January 2017, Martin Marietta filed a motion to dismiss the petition for

judicial review under North Carolina General Statute § 150B-46 and North Carolina

Rule of Civil Procedure 12 because it was not timely served on Martin Marietta. On

30 October 2017, the superior court denied Martin Marietta’s motion to dismiss.

North Carolina General Statute § 150B-46 (2017) provides, “Within 10 days after the

petition is filed with the court, the party seeking the review shall serve copies of the

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petition by personal service or by certified mail upon all who were parties of record to

the administrative proceedings.” According to the motion, the petition was filed on

28 December 2016, but Martin Marietta was not actually served until 17 January

2017. On 30 October 2017, the superior court denied Martin Marietta’s motion to

dismiss and extended the time for service.

Martin Marietta relies upon In re State ex rel. Employment Security

Commission, 234 N.C. 651, 68 S.E.2d 311 (1951), arguing Petitioner’s appeal must be

dismissed due to late service of the notice:

There is no inherent or inalienable right of appeal from an
inferior court to a Superior Court or from a Superior Court
to the Supreme Court.
A fortiori, no appeal lies from an order or decision of
an administrative agency of the State or from the
judgments of special statutory tribunals whose proceedings
are not according to the course of the common law, unless
the right is granted by statute. If the right exists, it is
brought into being, and is a right granted, by legislative
enactment.
There can be no appeal from the decision of an
administrative agency except pursuant to specific
statutory provision therefor.
Obviously then, the appeal must conform to the
statute granting the right and regulating the procedure.
The statutory requirements are mandatory and not
directory. They are conditions precedent to obtaining a
review by the courts and must be observed. Noncompliance
therewith requires dismissal.
....
This statement of the grounds of the appeal must be
filed within the time allowed for appeal. Its purpose is to
give notice to the Commission and adverse parties of the
alleged errors committed by the Commission and limit the

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scope of the hearing in the Superior Court to the specific
questions of law raised by the errors assigned. Clearly it
was intended, and must be construed, as a condition
precedent to the right of appeal. Noncompliance therewith
is fatal.

Id. at 653-54, 68 S.E.2d at 312 (emphasis added). Although the petition for judicial

review was timely filed, Martin Marietta contends because Petitioners failed to serve

the notice of appeal upon Martin Marietta within 10 days under North Carolina

General Statute § 150B-46, the superior court never obtained subject matter

jurisdiction. The superior court thus had no jurisdiction to extend the time for

service, so Martin Marietta’s motion to dismiss should have been allowed for lack of

subject matter jurisdiction.

We review a motion to dismiss for lack of subject matter jurisdiction de novo.

See Hardy ex rel. Hardy v. Beaufort Cty. Bd. of Educ., 200 N.C. App. 403, 408, 683

S.E.2d 774, 778 (2009) (“Subject matter jurisdiction is a prerequisite for the exercise

of judicial authority over any case or controversy. The standard of review on a motion

to dismiss under Rule 12(b)(1) for lack of subject matter jurisdiction is de novo.

(citation omitted)). While the file stamp is not legible on the petition for judicial

review, Martin Marietta concedes that the petition was filed with the superior court

on 28 December 2016, and thus within the time period established by North Carolina

General Statute § 150B-45 to invoke jurisdiction from the final decision entered on

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30 November 2016. See N.C. Gen. Stat. § 150B-45 (2017)3 (“To obtain judicial review

of a final decision under this Article, the person seeking review must file a petition

within 30 days after the person is served with a written copy of the decision.”). In NC

Department of Public Safety v. Owens, this Court held “that the superior court has

the authority to grant an extension in time, for good cause shown, to a party to serve

the petition beyond the ten days provided for under G.S. 150B–46.” 245 N.C. App.

230, 234, 782 S.E.2d 337, 340 (2016). Under Owens, the superior court had subject

matter jurisdiction and properly extended the time for service and thus denied the

motion to dismiss. See id. Because Martin Marietta raises only the issue of subject

matter jurisdiction in its brief, and not the substance of the good cause shown, we end

our analysis here. This argument is overruled.

B. Standing of Petitioners as “Persons Aggrieved”

Martin Marietta next contends that the superior court erred in determining

that petitioners were substantially prejudiced by DEQ’s issuance of the Permit.

At the outset, we must determine our standard of
review. That standard of review will depend upon the
nature of the error alleged in the petition for judicial
review. If errors of law are alleged, our review is de novo.
If the alleged error is that the final agency decision is not
supported by the evidence, we employ the whole record
test.

Curtis v. N.C. Dep’t of Transp., 140 N.C. App. 475, 478, 537 S.E.2d 498, 501 (2000)

3 North Carolina General Statute § 150B-45 was amended in 2018; the amendment does not affect this

case. See N.C. Gen. Stat. § 150B-45 (2018).

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(citations and quotation marks omitted).

North Carolina General Statute § 150B-23 provides,

(a) A contested case shall be commenced by
paying a fee in an amount established in G.S. 150B-23.2
and by filing a petition with the Office of Administrative
Hearings and, except as provided in Article 3A of this
Chapter, shall be conducted by that Office. The party who
files the petition shall serve a copy of the petition on all
other parties and, if the dispute concerns a license, the
person who holds the license. A party who files a petition
shall file a certificate of service together with the petition.
A petition shall be signed by a party, an attorney
representing a party, or other representative of the party
as may specifically be authorized by law, and, if filed by a
party other than an agency, shall state facts tending to
establish that the agency named as the respondent has
deprived the petitioner of property, has ordered the
petitioner to pay a fine or civil penalty, or has otherwise
substantially prejudiced the petitioner’s rights and that the
agency:
(1) Exceeded its authority or jurisdiction;
(2) Acted erroneously;
(3) Failed to use proper procedure;
(4) Acted arbitrarily or capriciously; or
(5) Failed to act as required by law or rule.
The parties in a contested case shall be given an
opportunity for a hearing without undue delay. Any person
aggrieved may commence a contested case hereunder.

N.C. Gen. Stat. § 150B-23(a) (2013) (emphasis added).4 Petitioners have not alleged

they were deprived of property or were ordered to pay a fine or civil penalty, and thus

they must show substantial prejudice. See id. North Carolina General Statute §

4 Subsection(f) was amended in 2018. See N.C. Gen. Stat. § 150B-23 (2018).

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150B-29 provides, “The party with the burden of proof in a contested case must

establish the facts required by G.S. 150B-23(a) by a preponderance of the evidence.”

N.C. Gen. Stat. § 150B-29 (2013). Thus, in this case, petitioners had to establish

substantial prejudice by a preponderance of the evidence. See N.C. Gen. Stat. §§

150B-23, -29.

In Empire Power Co. v. North Carolina Department of Environmental Health

and Natural Resources, our Supreme Court discussed the meaning of the term

“person aggrieved” in a case with a similar context, arising from issuance of a draft

air quality permit for a proposed turbine electric generating station. 337 N.C. 569,

572, 447 S.E.2d 768, 770 (1994). As explained in Empire Power Co.,

Under the NCAPA, any “person aggrieved” within
the meaning of the organic statute is entitled to an
administrative hearing to determine the person’s rights,
duties, or privileges. N.C.G.S. § 150B–23(a). “‘Person
aggrieved’ means any person or group of persons of
common interest directly or indirectly affected
substantially in his or its person, property, or employment,
by an administrative decision.” N.C.G.S. § 150B–2(6).
Under the predecessor judicial review statute, which did
not define the term, the Court gave it an expansive
interpretation:
The expression “person aggrieved” has
no technical meaning. What it means depends
on the circumstances involved. It has been
variously defined: “Adversely or injuriously
affected; damnified, having a grievance,
having suffered a loss or injury, or injured;
also having cause for complaint. More
specifically the word(s) may be employed
meaning adversely affected in respect of legal

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rights, or suffering from an infringement or
denial of legal rights.”
In re Assessment of Sales Tax, 259 N.C. at 595, 131 S.E.2d
at 446 (quoting 3 C.J.S. Aggrieved, at 509 (1973)). For the
following reasons, we conclude that Clark is a “person
aggrieved” as defined by the NCAPA within the meaning
of the organic statute.
Clark alleged that DEHNR issued the permit
allowing construction and operation of air emission sources
at the LCTS in violation of its statutory and regulatory
duties: to act on all permit applications “so as to effectuate
the [legislative] purpose . . . by reducing existing air
pollution and preventing, so far as reasonably possible, any
increased pollution of the air from any additional or
enlarged sources,” N.C.G.S. § 143–215.108(b); to reduce
levels of ozone pollution in the Mecklenburg County area;
to assess fully the impact of emissions of air pollutants
from the LCTS on levels of ozone pollution in Mecklenburg
County; to assess fully the impact of sulfur dioxide
emissions from the LCTS; to require air pollution control
technology adequate to control the emission of potentially
harmful pollutants from the LCTS; and to require Duke
Power to cause air quality offsets. Clark also alleged that
DEHNR issued the permit in violation of its statutory duty
to adequately address comments filed by Clark and other
members of the public during the public comment period.
Clark further alleged that, as the owner of property
immediately adjacent to and downwind of the site of the
proposed LCTS—which will emit tons of harmful air
pollutants if constructed and operated in accordance with
its air quality permit—he and his family will suffer injury
to their health, the value of their property, and the quality
of life in their home and their community.
In enacting the air pollution control provisions, the
General Assembly, as noted above, declared its intent
to achieve and to maintain for the citizens of
the State a total environment of superior
quality. Recognizing that the water and air
resources of the State belong to the people, the
General Assembly affirm[ed] the State’s

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ultimate responsibility for the preservation
and development of these resources in the
best interest of all its citizens and declare[d]
the prudent utilization of these resources to
be essential to the general welfare.
N.C.G.S. § 143-211. To further that intent, the General
Assembly mandated that standards of water and air purity
be designed, and programs implemented to achieve those
standards,
to protect human health, to prevent injury to
plant and animal life, to prevent damage to
public and private property, to insure the
continued enjoyment of the natural
attractions of the State, to encourage the
expansion of employment opportunities, to
provide a permanent foundation for healthy
industrial development and to secure for the
people of North Carolina, now and in the
future, the beneficial uses of these great
natural resources.
Id. (emphasis added).
Clearly, Clark alleged sufficient injury in fact to
interests within the zone of those to be protected and
regulated by the statute, and rules and standards
promulgated pursuant thereto, the substantive and
procedural requirements of which he asserts the agency
violated when it issued the permit. As an adjacent property
owner downwind of the LCTS, Clark may be expected to
suffer from whatever adverse environmental consequences
the LCTS might have. In addition, a judgment in favor of
Clark would substantially eliminate or redress the injury
likely to be caused by the decision to permit Duke Power to
build the LCTS. Clark therefore is a “person aggrieved”
within the meaning and intent of the air pollution control
act. See Orange County v. Dept. of Transportation, 46 N.C.
App. 350, 360–62, 265 S.E.2d 890, 898–99, disc. rev. denied,
301 N.C. 94 (1980) (plaintiffs were all “aggrieved,” within
the meaning of the NCAPA provision, by a decision of the
State Board of Transportation on the location of an
interstate highway where the individual plaintiffs were

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property owners within the proposed corridor of the
highway, the members of plaintiff non-profit corporation
were citizens and taxpayers who lived in or near the
proposed highway corridor, plaintiff county’s tax base and
planning jurisdiction would be affected, and individual
plaintiffs would be affected as taxpayers; further, the
“procedural injury” implicit in the failure of an agency to
prepare an environmental impact statement was itself a
sufficient “injury in fact” to support standing as an
“aggrieved party” under former N.C.G.S. § 150A–43, as
long as such injury was alleged by a plaintiff having
sufficient geographical nexus to the site of the challenged
project that he might be expected to suffer whatever
environmental consequences the project might have); State
of Tennessee v. Environmental Management Comm., 78
N.C. App. 763, 766–67, 338 S.E.2d 781, 783 (1986) (a
consent special order issued by respondent agency to a
corporation allowing it to discharge effluents into a river
was issued without a hearing and by its own terms
purported to take precedence over the terms of a proposed
National Pollutant Discharge Elimination System permit
to the corporation, so that the right of petitioner to be heard
was impaired; petitioner therefore qualified as an
“aggrieved person” for purposes of judicial review; further,
petitioner alleged that its property rights in the river were
affected, and these allegations also established petitioner's
“aggrieved person” status); see generally 2 Am. Jur. 2d
Administrative Law §§ 443–50 (1994) (“Persons Adversely
Affected or Aggrieved”).

Id. at 588-90, 447 S.E.2d at 779-81 (alterations in original) (emphasis added).

Here, similar to Empire Power Co. and the cases quoted within Empire,

Petitioners alleged substantial prejudice in that the Permit was issued without

compliance with applicable regulations in that Martin Marietta’s “proposed discharge

of 12 million gallons of mine wastewater per day into Blounts Creek would displace

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native fish, macroinvertebrates (insects, mollusks, crayfish, etc.) and plants[,]” and

the wastewater would cause “higher flow and velocity, near neutral pH, and low

tannin levels” meaning Blounts Creek would no longer qualify as swamp waters. See

generally id.

More specifically, one of the individuals who filed an affidavit in support of

Petitioners, Mr. Jimmy Daniels, averred that he was a member of the Pamlico-Tar

River Foundation and both his “home and business, [“Cotton Patch Landing, a boat

ramp and marina,”] are right on the banks of Blounts Creek.” Mr. Daniels described

in detail the biodiversity in Blounts Creek and how it draws people “from all across

the state[.]” Mr. Daniels averred that he boated “a couple of times a week” and

enjoyed the wildlife diversity; through Cotton Patch Landing, he sells fishing

supplies, stores and maintains boats, and engages in commercial activities involving

his boat ramp. Mr. Daniels also noted the hundreds of thousands of dollars he has

invested into his business and stated that based on his experience with Blounts

Creek, he believed Martin Marietta’s wastewater being dumped “into the

headwaters” “will change the way the whole system works.” Mr. Daniels explained

specifically why and how the wastewater would affect his business and personal

interests and noted “word of mouth concerning the discharge” had already had a

negative effect on Cotton Patch Landing when a fishing tournament previously held

at Cotton Patch Landing was moved due to fears over how the wastewater would

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impact fishing for the tournament. Mr. Daniels noted Cotton Patch Landing lost

approximately $5,000 from the tournament move. Again, Mr. Daniels is but one of

many affiants noting similar issues with the wastewater being dumped into Blounts

Creek. We view the interests of Mr. Daniels and other affiants about wastewater in

Blounts Creek to be similar to the complainant in Empire Power Co., who alleged,

as the owner of property immediately adjacent to and
downwind of the site of the proposed LCTS—which will
emit tons of harmful air pollutants if constructed and
operated in accordance with its air quality permit—he and
his family will suffer injury to their health, the value of
their property, and the quality of life in their home and
their community.

Id. at 589, 447 S.E.2d at 780.

While Martin Marietta contends that Petitioner’s alleged prejudice amounts

only to speculation as to the effects of the discharge of water allowed by the Permit,

allegations as to potential prejudice here are no different from the allegations of

potential air pollution in Empire Power Co., as the actual effects cannot be known for

certain until the discharge occurs. See generally id., 337 N.C. 569, 447 S.E.2d 768.

In addition, this Court has clarified that in a challenge based upon an alleged failure

of an agency or department of the State to follow its own guidelines, the prejudice

standard differs from that in other types of civil cases. See, e.g., N.C. Forestry Ass’n

v. N.C. Dep’t of Env’t & Natural Res., Div. of Water Quality, 357 N.C. 640, 644, 588

S.E.2d 880, 882–83 (2003) (“In general, individuals adversely affected by a

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discretionary agency decision generally have standing to complain that the agency

based its decision upon an improper legal ground.” (citation and quotation marks

omitted)). Otherwise the burden of showing substantial prejudice would be “nearly

impossible”:

Because the substance of those policies required the
Department to consider a number of discretionary factors,
however, we pointed out that a showing of prejudice would
be “nearly impossible” for the petitioner to achieve.
Specifically, we observed that
to show prejudice from failure to follow policy,
the petitioner would have to show, not only
how he stood in relation to other employees in
the same class as to type of appointment,
length of service, and work performance, but
he would have to show the weight which the
Department would attribute to each of those
factors. The Commission and the reviewing
court would be relegated to speculating how
the Department would weigh each factor.
Therefore, we held that it was sufficient to show prejudice
for the petitioner to establish that the Department failed
to follow the mandatory policies of the Commission, which
had been promulgated pursuant to statutory authority. A
separate showing of prejudice was unnecessary in that
circumstance.

Surgical Care Affiliates, LLC v. N.C. Dep’t of Health & Human Servs., 235 N.C. App.

620, 627, 762 S.E.2d 468, 473 (2014) (citations and brackets omitted).

Here, Petitioners alleged that the Division of Water Resources violated its own

applicable regulations by issuing the Permit to Martin Marietta which authorized

“the discharge of 12 million gallons of mine wastewater into tributaries of Blounts

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Creek each day.” Petitioners have alleged DEQ failed to follow its own policies in

issuing the Permit and that the discharge of wastewater into Blounts Creek, if done

in a manner not in compliance with the applicable regulations, would damage the

water quality, the fish and other biota in Blounts Creek, and the personal and

commercial benefits derived from Blounts Creek. Petitioners are “within the zone of

those to be protected and regulated by the statute, and rules and standards

promulgated pursuant thereto, the substantive and procedural requirements of

which he asserts the agency violated when it issued the permit.” Empire Power Co.,

337 N.C. at 589, 447 S.E.2d at 780. The superior court did not err in concluding

Petitioners demonstrated their rights were substantially prejudiced and thus they

are “person[s] aggrieved[.]” Id. at 590, 447 S.E.2d at 780. This argument is

overruled.5

5 Implicit in this holding is also a rejection of Martin Marietta’s argument that “North Carolina courts

have held that only the state, and not individual plaintiffs, can enforce public trust rights” such as
interests in fishing, boating, and recreation. As DEQ acknowledges, the cases Martin Marietta cites
for this proposition are inapposite. This is not a claim under public trust doctrine or any other common
law action, see Town of Nags Head v. Cherry, Inc., 219 N.C. App. 66, 723 S.E.2d 156 (2012); Fish House,
Inc. v. Clarke, 204 N.C. App. 130 (2010), but instead a request for review of an agency action pursuant
to the North Carolina Administrative Procedure Act. In such an action, the organic statute at issue
defines the rights, duties, and privileges that provide the grounds for the administrative hearing.
Empire Power Co., 337 N.C. at 583, 447 S.E.2d at 583. North Carolina’s water quality statutes and
associated rules specifically protect water quality for recreational uses. See, e.g., N.C. Gen. Stat. §
143-214.1(3) (year) (directing adoption of water quality standards and classifications that consider the
use and value of waters of the state for “recreation”); 15A NCAC 02b.0101(c)(1) (stating Class C are
freshwaters protected for “secondary recreation” and “fishing”). Petitioners “interests in the waters
affected” by the discharge at issue “are discrete and particular to [its] certain members who live near,
or who visit, fish, or shellfish in the affected waters, and are not merely a generalized public interest.”
Holly Ridge Assoc., LLC v. N.C. Dept’ of Env’t & Natural Resources, 176 N.C. App. 594, 603, 627 S.E.2d
326, 333 (2006), rev’d on other grounds, 361 N.C. 531, 648 S.E.2d 830 (2007).

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III. Substantive Issues regarding Permit

We now turn to the substantive issues regarding issuance of the Permit.

A. Standard of Review

Petitioners raised three arguments regarding DEQ’s failure to ensure

compliance with applicable water quality standards. The superior court determined

that the ALJ’s order was in error only as to the findings and conclusion regarding

that DEQ ensured “reasonable compliance with the biological integrity standard as

set forth in 15A N.C.A.C. 02B .211(2), 0220(2), and 0202(11)[,]” and DEQ and Martin

Marietta appeal this determination. The superior court affirmed the ALJ’s findings

and conclusions regarding the other standards – swamp waters and pH standards–

and Petitioners cross-appealed these determinations. We will therefore address the

arguments as to each substantive issue in the order as addressed by the superior

court.

The North Carolina Administrative Procedure Act
(APA), codified at Chapter 150B of the General Statutes,
governs trial and appellate court review of administrative
agency decisions. The APA provides a party aggrieved by
a final decision in a contested case a right to judicial review
by the superior court. N.C. Gen. Stat. §§ 150B–43 and –50
(2017). A party to the review proceeding in superior court
may then appeal from the superior court’s final judgment
to the appellate division. N.C. Gen. Stat. § 150B–52 (2017).
The APA sets forth the scope and standard of review for
each court.

EnvironmentaLEE v. Dept of Environment, 258 N.C. App. 590, 595, 813 S.E.2d 673,

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677 (2018).

When a superior court exercises judicial review over
an agency’s final decision, it acts in the capacity of an
appellate court. The APA limits the scope of the superior
court’s judicial review as follows:
(b) The court reviewing a final decision may
affirm the decision or remand the case for further
proceedings. It may also reverse or modify the
decision if the substantial rights of the petitioners
may have been prejudiced because the findings,
inferences, conclusions, or decisions are:
(1) In violation of constitutional
provisions;
(2) In excess of the statutory authority or
jurisdiction of the agency or administrative
law judge;
(3) Made upon unlawful procedure;
(4) Affected by other error of law;
(5) Unsupported by substantial evidence
admissible under G.S. 150B-29(a), 150B-30,
or 150B-31 in view of the entire record as
submitted; or
(6) Arbitrary, capricious, or an abuse of
discretion.
N.C. Gen. Stat. § 150B-51 (2017). The superior court’s
standard of review is dictated by the nature of the errors
asserted. The APA sets forth the standard of review to be
applied by the superior court as follows.
(c) In reviewing a final decision in a contested
case, the court shall determine whether the
petitioner is entitled to the relief sought in the
petition based upon its review of the final decision
and the official record. With regard to asserted
errors pursuant to subdivisions (1) through (4) of
subsection (b) of this section, the court shall conduct
its review of the final decision using the de novo
standard of review. With regard to asserted errors
pursuant to subdivisions (5) and (6) of subsection (b)
of this section, the court shall conduct its review of

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the final decision using the whole record standard of
review.
N.C. Gen. Stat. § 150B–51(c).

Id. at 595-96, 813 S.E.2d at 677–78 (citations, quotation marks, and brackets

omitted).

Our Supreme Court has observed that the first four
grounds enumerated under this section may be
characterized as law-based inquiries, whereas the final two
grounds may be characterized as fact-based inquiries.
Moreover, it is well settled that in cases appealed from
administrative tribunals, questions of law receive de novo
review, whereas fact-intensive issues such as the
sufficiency of the evidence to support an ALJ’s decision are
reviewed under the whole record test.
Under the de novo standard of review, the Court
considers the matter anew and freely substitutes its own
judgment. However, our Supreme Court has made clear
that even under our de novo standard, a court reviewing a
question of law in a contested case is without authority to
make new findings of fact. Under the whole record test,
the reviewing court may not substitute its judgment for the
ALJ’s as between two conflicting views, even though it
could reasonably have reached a different result had it
reviewed the matter de novo. Instead, we must examine
all the record evidence—that which detracts from the ALJ’s
findings and conclusions as well as that which tends to
support them—to determine whether there is substantial
evidence to justify the ALJ’s decision. Substantial
evidence is relevant evidence a reasonable mind might
accept as adequate to support a conclusion. We undertake
this review with a high degree of deference because it is
well established that
in an administrative proceeding, it is the
prerogative and duty of the ALJ, once all the
evidence has been presented and considered,
to determine the weight and sufficiency of the
evidence and the credibility of the witnesses,

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to draw inferences from the facts, and to
appraise conflicting and circumstantial
evidence. The credibility of witnesses and the
probative value of particular testimony are for
the ALJ to determine, and the ALJ may
accept or reject in whole or part the testimony
of any witness.

N. Carolina Dep’t of Pub. Safety v. Ledford, 247 N.C. App. 266, 286–87, 786 S.E.2d

50, 63–64 (2016) (citations, quotation marks, and brackets omitted).

This Court reviews the superior court’s order to determine if the superior court

applied the correct standard of review based upon the “grounds for reversal or

modification” argued before the superior court. EnvironmentaLEE, 258 N.C. App. at

598, 813 S.E.2d at 678-79.

[I]n reviewing a superior court order examining an agency
decision, an appellate court must determine whether the
agency decision (1) violated constitutional provisions; (2)
was in excess of the statutory authority or jurisdiction of
the agency; (3) was made upon unlawful procedure; (4) was
affected by other error of law; (5) was unsupported by
substantial admissible evidence in view of the entire
record; or (6) was arbitrary, capricious, or an abuse of
discretion. N.C. Gen. Stat. § 150B–51 (2001). In
performing this task, the appellate court need only
consider those grounds for reversal or modification raised
by the petitioner before the superior court and properly
assigned as error and argued on appeal to this Court.

Id.

B. Applicable Regulations and Definitions

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North Carolina General Statute § 143-214.1 directs the North Carolina

Environmental Management Commission to classify all bodies of water6 in the state

and to adopt standards for each classification. See N.C. Gen. Stat. § 143-214.1 (2013),

see also N.C. Gen. Stat. § 143-212 (2013). One body of water may include areas with

different primary classifications and supplemental classifications, depending upon

“the existing or contemplated best usage of the various streams and segments of

streams in the basin, as determined through studies and evaluations and the holding

of public hearings for consideration of the classifications proposed.” 15A N.C.A.C.

2B.0301 (2013). The water quality standards applicable to a body of water are

determined by the classification. See generally 15A N.C.A.C. 2B.0301 (2013). The

primary classification of the portion of Blounts Creek at issue is Class C along with

supplemental classifications of Sw (“swamp waters”) and NSW (“nutrient sensitive

waters”). See generally 15A N.C.A.C. 2B.0101, .0301 (2013).

Class C classification is appropriate for “freshwaters protected for secondary

recreation, fishing, aquatic life including propagation and survival, and wildlife. All

freshwaters shall be classified to protect these uses at a minimum.” 15A N.C.A.C.

2B.0101 (2013). Sw classification applies to “waters which have low velocities and

6 “(6) ‘Waters’ means any stream, river, brook, swamp, lake, sound, tidal estuary, bay, creek, reservoir,

waterway, or other body or accumulation of water, whether surface or underground, public or private,
or natural or artificial, that is contained in, flows through, or borders upon any portion of this State,
including any portion of the Atlantic Ocean over which the State has jurisdiction.” N.C. Gen. Stat. §
143-212(6) (2013).

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other natural characteristics which are different from adjacent streams.” Id. NSW

classification applies to “waters subject to growths of microscopic or macroscopic

vegetation required limitations on nutrient inputs.” Id. More specifically, as to

supplemental classifications, Sw is defined to “mean those waters which are classified

by the Environmental Management Commission and which are topographically

located so as to generally have very low velocities and other characteristics which are

different from adjacent streams draining steeper topography.” 15A N.C.A.C.

2B.0202. Nsw is defined to “mean those waters which are so designated in the

classification schedule in order to limit the discharge of nutrients (usually nitrogen

and phosphorus).” Id.

As for the broader classification of Class C, those water quality standards are

provided in 15A N.C.A.C. 2B.0211, entitled “FRESH SURFACE WATER QUALITY

STANDARDS FOR CLASS C WATERS[.]” See 15A N.C.A.C. 2B.0211. For Class C

waters, pH “shall be normal for the waters in the area, which range between 6.0 and

9.0 except that swamp waters may have a pH as low as 4.3 if it is the result of natural

conditions[.]” Id. The “Best Usage” of Class C waters is “aquatic life propagation and

maintenance of biological integrity (including fishing and fish), wildlife, secondary

recreation, agriculture, and any other usage except for primary recreation or as a

source of water supply for drinking, culinary, or food processing purposes[.]” Id.

“Conditions Related to Best Usage” note “the waters shall be suitable for aquatic life

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Opinion of the Court

propagation and maintenance of biological integrity, wildlife, secondary recreation,

and agriculture. Sources of water pollution which preclude any of these uses on either

a short-term or long-term basis shall be considered to be violating a water quality

standard.” Id.

C. Biological Integrity

The trial court reversed the portion of the ALJ’s final decision regarding DEQ’s

compliance with the biological integrity standards. Martin Marietta contends the

superior court “Failed To Defer to DWR, Misinterpreted the Biological Integrity

Standard, and Improperly Found Facts[.]” In other words, respondents argue the

trial court made an error of law by misinterpreting the requirements of the applicable

regulations as to “biological integrity;” misunderstood the science behind the

applicable regulations; and failed to use the proper standard of review in addressing

the issues before it. Martin Marietta specifically contends,

The Superior Court failed to defer to DWR as it is
required to do, misunderstood the permitting rules and
what DWR did, and reversed the ALJ’s holding on
biological integrity under the following erroneous analysis:
(1) “DWR must protect the indigenous community”; (2) the
“plain language” of the standard establishes “base line
metrics” that must be “determined” or “measured” to apply
the standard properly; and (3) without “determining the
base line metrics,” DWR “could not ensure reasonable
compliance” [sic] with the standard.

(Ellipses omitted.)

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Petitioners argue the superior court correctly interpreted the biological

integrity standard:

The issue before the Court is one of law: does the
biological integrity standard require DWR to measure the
terms in the rule and to protect the indigenous community
of fish, insects, and other animals that live in Blounts
Creek? The Superior Court recognized that under the
lawful interpretation of the rule, DWR must measure the
terms in the standard and establish specific reference
conditions before issuing a permit.

As the interpretation of the biological integrity standard applied by the superior court

is an issue of law, we review this determination de novo. N. Carolina Dep’t of Pub.

Safety, 247 N.C. App. at 286, 786 S.E.2d at 63.

This issue requires consideration of how DEQ measures and evaluates

“biological integrity” as part of its general duties in protecting water quality and in

the context of issuance of a Permit. The ALJ made extensive findings of fact and

conclusions of law on this issue,7 many of which Petitioners challenge:

44. Petitioners claim that, in issuing the NPDES
Permit, DWR failed to reasonably ensure compliance with
the biological integrity standard.

7 In Petitioners’ brief to the superior court Petitioners challenge the findings of fact and conclusions of

law in such a manner that it is difficult to keep track of what actually is at issue before the court. For
instance, in paragraph 81 of Petitioners’ brief they challenge findings of fact “19, 23-25,” and then in
paragraph 82 they challenge findings of fact “17-20, 22-25[,]” the latter which obviously encompasses
the former and broadens it; this is but one of many such examples. Petitioners have divided their
challenges based upon the topic they deem to be at issue, but for this Court’s purposes we simply note
that Petitioners challenged many of the ALJ’s substantive findings of fact and conclusions of law as to
biological integrity, but the challenges were so extensive we have not listed all of them, although we
have considered all.

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45. Under applicable North Carolina rules, one of the
existing uses of all classified surface waters is
“maintenance of biological integrity.” See 15A NCAC 02B
.0211(1) (2013) (freshwater), and 02B .0220(1) (2013)
(saltwater).

46. The term “biological integrity” is defined in 15A
NCAC 02B .0202(11) as follows: “the ability of an aquatic
ecosystem to support and maintain a balanced and
indigenous community of organisms having species
composition, diversity, population densities and functional
organization similar to that of reference conditions.”

47. The biological integrity standards applicable to
upper and lower Blounts Creek state:
the waters shall be suitable for aquatic life
propagation and maintenance of biological
integrity . . . . Sources of water pollution
which preclude any of these uses on either a
short-term or long-term basis shall be
considered to be violating a water quality
standard . . . .
15A NCAC 02B .0211(2) (2013) (freshwater standard). See
also 15A NCAC 02B .0220(2) (2013) (same standard for
saltwater).

48. DWR interprets the applicable rules and definitions
to mean that an NPDES permit complies with the
biological integrity standard if the permit’s terms and
conditions reasonably ensure that the permitted discharge
will not preclude maintenance of the ability of an aquatic
ecosystem to support and maintain a balanced and
indigenous community of organisms having species
composition, diversity, population densities and functional
organization similar to that of reference conditions.

49. The biological integrity standard is administered by
DWR and relates to a highly technical and scientific subject
area within DWR’s expertise.

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50. As required by North Carolina case law and the
APA, the undersigned accords deference and gives due
regard to DWR’s interpretation of its own rules.

51. Even if the undersigned were not required to defer
to DWR’s interpretation of the biological integrity standard
rules, the undersigned finds that DWR’s interpretation is
longstanding, is reasonable, and is consistent with and
supported by the plain language of the rules, and therefore
the undersigned will decide Petitioners’ biological integrity
claim based on DWR’s interpretation of the rules.

52. The preponderance of the evidence shows that, in
evaluating and determining whether the NPDES Permit
reasonably ensures compliance with the biological
integrity standard, DWR (through its staff) applied its
knowledge and expertise, and:
a. identified the Blounts Creek system, meaning
Blounts Creek and its tributaries, as the appropriate
“aquatic ecosystem”;
b. determined that the appropriate “reference
conditions” were the existing conditions of the
Blounts Creek system before the proposed
discharge;
c. studied and assessed the existing, pre-
discharge ecological resources of the Blounts Creek
system;
d. determined the degree and geographic scope
of potential physical and chemical impacts of the
proposed discharge;
e. determined the predicted changes to the
ecosystem and ecological resources from the
proposed discharge to be limited; and
f. concluded that the effects predicted to occur
as a result of the permitted discharge would not
violate the standard, and, in fact, a violation would
not occur unless the impacts to the Blounts Creek
aquatic ecosystem were much greater in degree and
geographic scope than those predicted to occur.

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53. Petitioners’ arguments that DWR misinterpreted
and misapplied key aspects of the biological integrity
standard and understated the effects of the permitted
discharge present questions of law and fact, and mixed
questions of law and fact. Petitioners’ arguments have
been thoroughly considered and rejected by the
undersigned as unpersuasive and unsupported by the
preponderance of evidence.

“Aquatic Ecosystem”

54. Petitioners have asserted that the relevant “aquatic
ecosystem” should be defined more narrowly and that DWR
must use a single stream segment as the ecosystem unit for
assessing compliance. See Petition at 3.

55. The term “aquatic ecosystem” is not defined by
North Carolina statute or rule.

56. The determination and application of “aquatic
ecosystem” in a specific context is complex and requires
significant scientific expertise and judgment, and should be
accorded deference. See County of Durham v. N.C. Dept.
of Environment and Natural Resources, 131 N.C. App. at
396-97, 507 S.E.2d at 311 (1998), disc. rev. denied, 350 N.C.
92, 528 S.E.2d 361 (1999).

57. DWR’s interpretation and application of this term
are reasonable, rational, and in accordance with the
language and purpose of the biological integrity standard.

58. To the extent DWR’s selection of an appropriate
aquatic ecosystem is considered a factual determination, it
is one which falls directly within the agency’s expertise and
is therefore entitled to “due regard” pursuant to the APA.

“Reference Conditions”

59. Petitioners have asserted that DWR failed to
conduct a biological integrity analysis by inadequately

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sampling for “species composition, diversity, population
densities and functional organization” throughout the
Blounts Creek aquatic ecosystem.

60. The determination and application of “reference
conditions” in a specific context is complex and requires
significant scientific expertise and judgment, and should be
accorded deference.

61. DWR’s interpretation and application of this term
are reasonable, rational, and in accordance with the
language and purpose of the biological integrity standard.

62. To the extent DWR’s selection of appropriate
“reference conditions” is considered a factual
determination, it is one which falls directly within the
agency’s expertise and is therefore entitled to “due regard”
pursuant to the APA.

63. The preponderance of the evidence shows that
Blounts Creek aquatic ecosystem’s existing conditions
(“reference conditions”) are dynamic, vary over time and
geographic location, and can be affected by many
environmental factors.

64. The preponderance of the evidence shows that DWR
had sufficient information such that the biological
sampling efforts Petitioners sought were unnecessary.

65. Before issuing the Permit, DWR determined that:
(a) the proposed discharge likely would not cause
significant erosion or sedimentation; (b) pH likely would
not exceed 6.9 in the upper Blounts Creek and was unlikely
to change significantly in lower Blounts Creek; (c) relative
salinity impacts would likely be on the order of 1 ppt and
salinities would remain within the variability of the
system; (d) shifts in macrobenthic invertebrates would
likely be toward an increase in diversity and would be
geographically limited to the upper reaches of Blounts
Creek; and (e) the proposed discharge is not likely to

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adversely impact fish communities of the Blounts Creek
aquatic ecosystem. These determinations by DWR are
reasonable and supported by the preponderance of the
evidence.

66. DWR determined that the likely effects of the
permitted discharge are limited in degree, limited in
geographic scope, and not deleterious.

67. The preponderance of the evidence supports DWR’s
conclusion and shows that the permitted discharge will not
have any significant detrimental effect on the Blounts
Creek aquatic ecosystem, including the many miles of C
and Sw stream segments of other tributaries of Blounts
Creek.

Impacts of the Proposed Discharge

68. Petitioners argued that DWR underestimated or
understated the effects the proposed discharge will likely
have on the Blounts Creek aquatic ecosystem, including
effects on flow, pH, salinity, benthos, fish, and the existing
biological community of Blounts Creek.

69. DWR’s findings and inferences regarding the
predicted effects of the proposed discharge fall within
“specialized knowledge of the agency.” As such, the
undersigned is required to give such facts and inferences
“due regard” pursuant to the APA. N.C. Gen. Stat. § 150B-
34(a).

70. The preponderance of the evidence demonstrates
that DWR applied its knowledge and expertise in its
collection and review of the data and reports obtained
during the permitting process, and drew reasonable
inferences and conclusions based on those data and
reports.

71. The preponderance of the evidence demonstrates
that DWR reasonably evaluated and adopted the findings

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of the Kimley Horn reports (Exs. R13, R15) and the CZR
report (Ex. R16) after satisfying itself of the reliability of
these studies.

72. The preponderance of the evidence demonstrates
that: (a) DWR applied its discretion and expertise in its
review of the comments it received from the public
(including Petitioners[]), EPA, and other state agencies
during the permitting process; and (b) the substantive
comments were considered and accounted for by DWR
based on DWR’s expertise, judgment, and rational
evaluation of the comments and other evidence.

73. To the extent Petitioners contend that DWR acted
arbitrarily and capriciously in its evaluation of the
evidence, its gathering and evaluation of relevant data and
information, its interpretation and application of the
biological integrity standard, and its conclusion that the
NPDES Permit reasonably ensures compliance with the
biological integrity standard, Petitioners failed to present
any evidence that DWR acted “whimsically” or in “bad
faith.”

74. The undersigned finds that DWR’s evaluation of the
NPDES permit application, reports and data submitted
during the permit process, the data independently collected
by DWR, and the comments received from the public, state
agencies and EPA was reasonable, rational, thorough,
supported by a preponderance of the evidence in the record,
and undertaken in good faith.

75. The undersigned finds the evidence and expert
opinion testimony as well as the lay opinion testimony,
even if admitted, presented by Petitioners, does not
overcome DWR’s determinations, with respect to the likely
impacts and effects of the permitted discharge, which were
thoroughly evaluated based on DWR’s knowledge,
expertise, and judgment, and well-supported by a
preponderance of the evidence.

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76. The undersigned has considered all of the evidence
of potential impacts presented by Petitioners and their
experts, and finds, based on a preponderance of the
evidence, that Petitioners’ evidence either does not
contradict DWR’s determinations or is not persuasive and
not sufficient to overcome the data, studies, and other
information reasonably considered and relied on by DWR
in evaluating compliance with the biological integrity
standard.

77. Petitioners failed to present evidence sufficient to
overcome the presumption that DWR acted appropriately
in determining the NPDES Permit reasonably ensures
compliance with the biological integrity standard.

78. The preponderance of the evidence demonstrates
that DWR:
a. reasonably interpreted the biological
integrity standard;
b. reasonably and rationally applied the
biological integrity standard to the relevant
information and facts regarding the proposed
discharge;
c. reasonably determined that, although certain
changes are predicted to occur as a result of the
proposed discharge, the predicted effects would not
preclude the ability of the relevant aquatic
ecosystem to support and maintain a balanced and
indigenous community of organisms having species
composition, diversity, population densities and
functional organization similar to that of reference
conditions; and
d. reasonably and rationally determined that
the NPDES Permit reasonably ensures compliance
with the biological integrity standard.

79. Petitioners failed to meet their burden of proving by
a preponderance of the evidence that DWR exceeded its
authority or jurisdiction, acted erroneously, failed to use
proper procedure, acted arbitrarily or capriciously, or failed

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to act as required by law or rule in determining the NPDES
Permit reasonably ensures compliance with the biological
integrity water quality standard. See 15A NCAC 02B.
0202(11), 15A NCAC 02B .0211(2) (2013), and 15A NCAC
02B .0220(2) (2013).

80. DWR’s decision that the NPDES Permit reasonably
ensures compliance with the biological integrity water
quality standard is affirmed.

The superior court did not determine that any of the findings of fact made by

the ALJ were unsupported by the record, but instead determined on de novo review

that DWR’s interpretation of the “biological integrity standard rules and related

definitions” was not reasonable and was “contrary to the language of the standard

and definitions.” The superior court rejected both DEQ’s and the ALJ’s interpretation

of the biological integrity standard, and Martin Marietta and DEQ challenge this

conclusion on appeal as reflected in their arguments that the superior court “Failed

To Defer to DWR, Misinterpreted the Biological Integrity Standard, and Improperly

Found Facts[:]8”

Class C waters must be “suitable for aquatic life
propagation and maintenance of biological integrity”
among other uses. 15A NCAC 02B.0211(2) The term
“Biological Integrity” is defined by 15A NCAC 02B.202(11)
as “the ability of an aquatic ecosystem to support and
maintain a balanced and indigenous community of
organisms having species composition, diversity,
population densities and functional organization similar to
that of reference conditions”.
The rules do not define the terms “species

8 The following quote from the superior court order arguably includes some findings of fact, but the

superior court stated its decision as based upon de novo review of a legal issue.

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composition”, “diversity”, “population densities” or
“functional organization”. Dr. Overton was offered and
accepted by the AU as an expert in the field of fisheries
ecology, larval fish ecology, fisheries management, and fish
sampling methods and analysis. He testified that species
composition counts the number of species in a system.
Species diversity counts the number species present and
the relative abundance of each species. Population density
describes how many individuals are in a defined area and
functional organization describes the organization of
biological community.
Tom Reeder with DWR testified that he did not
know if there was such a thing as a biological integrity
analysis; that he had never really heard of such a thing.
He further testified that no statutes or rules set forth
numeric standards or explicit methods or metrics by which
DWR must make a determination that a NPDES permit
reasonably ensures compliance with the biological
integrity standard. Rather, the standard requires DWR to
exercise its discretion, expertise and professional judgment
to determine whether the anticipated impacts of a proposed
discharge are such that the discharge will preclude the
ability of an “aquatic ecosystem” to support and maintain
a balanced and indigenous community of organisms having
species composition, diversity, population densities, and
functional organization “similar” to that of “reference
conditions”. DWR staff conceded that the agency did not
evaluate species composition, diversity, population
density, or functional organization in Blounts Creek. Mr.
Reeder justified the failure to evaluate these metrics by
saying that he considered the impact of the permitted
discharge to be de minimus. In essence the agency reached
the ultimate conclusion that the impact of the permitted
discharge was de minimus first, without evaluating species
composition, diversity, population density, and functional
organization, and then used the ultimate conclusion to
conclude that evaluation of the metrics was unnecessary.
With respect to questions of law, the reviewing court
employs a de novo review. When applying de novo review,
the Court may freely substitute its judgment for that of the

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agency. In re Appeal of N. C. Sav. & Loan League, 302 N.
C. 458 (1981) Incorrect statutory interpretation is an error
of law which allows the court to apply a de novo review.
Brooks v. Rebarco, 91 N.C. App. 459 (1988) However even
when reviewing a case de novo courts recognize the
longstanding tradition of according deference to an
agency’s interpretation of its rules. A reviewing Court
should defer to agency’s interpretation of a statutes or
rules it administers so long as the agency interpretation is
reasonable and based upon a permissible construction of
the statute or rule. County of Durham v. N.C. Dep’t of Env’t
and Natural Res., 131 N.C. App. 395 (1998).
Interpretations that conflict with the clear intent and
purpose of the law are entitled to no deference. Burgess v.
Your House of Raleigh, Inc., 326 N.C. 205 (1990) An
agency’s interpretation of its own regulations will be in
enforced unless clearly erroneous or inconsistent with the
regulation’s plain language. WASCO LLC. V. N.C. Dep’t of
Env’t & Natural Res., 799 S.E. 2nd 405 (2017)
The terms “species composition, diversity,
populations densities, and functional organization” used in
the biological integrity standard must be given meaning.
Kyle v. Holston Group, 188 N.C. App. 686 (2008) The
standard requires DWR to maintain the indigenous
biological community by insuring that the post discharge
“species composition, diversity, population densities, and
functional organization are similar to that of reference
conditions” determined before the discharge is permitted.
The rule is clear that referenced conditions must be
evaluated on the basis of and as defined in those terms. Yet
the DWR staff conceded that they did not measure any of
the biological integrity metrics in Blounts Creek when
evaluating the permit’s compliance with the standard.
Thus, DWR failed to determine the base line metrics
required by 15A NCAC 02B.0202(11) and could not,
therefore, ensure reasonable compliance with the biological
integrity standard.
The Biological integrity standard is clear; DWR
must protect the indigenous community by determining
reference conditions in terms of an evaluated impacts on

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the community’s species composition, diversity, population
density and functional organization. Reference conditions
must be specific enough to allow the agency to apply the
biological integrity standard properly. DWR failed to apply
the plain language of the biological integrity standard.
Therefore DWR did not “reasonably ensure compliance
with” the biological integrity standard. Consequently the
agency exceeded its authority and erred as a matter of law
when issuing the permit. Based upon a de novo review of
the biological integrity standard rules and related
definitions the Court concludes that DWR’s interpretation
of the rule is not reasonable and is contrary to the language
of the standard and definitions.
Conclusions of law 51 through 53, 61, 62, 64 through
67,70, 75, 77 through 80, 110 through 112 are reversed. 9

Ultimately, the superior court determined, contrary to the ALJ’s conclusion,

that DEQ’s interpretation of the biological integrity standard was not reasonable and

was contrary to the language of the standard and definitions. The superior court did

not determine that the ALJ’s findings of fact were unsupported by substantial

evidence but instead found legal error as to the meaning and application of the

biological integrity standard. The primary difference between the ALJ’s order and

the superior court’s order is its determination of the “clear” meaning of the biological

integrity standard and its resulting determination not to defer to agency expertise.

Again, the superior court concluded that

[t]he Biological integrity standard is clear; DWR
must protect the indigenous community by determining
reference conditions in terms of an evaluated impacts on
the community’s species composition, diversity, population

9 This section is quoted as it was in the record before us, including spacing and punctuation.

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density and functional organization. Reference conditions
must be specific enough to allow the agency to apply the
biological integrity standard properly. DWR failed to apply
the plain language of the biological integrity standard.

But as the superior court notes, many of the operative words in the applicable

regulations are not defined. Despite the superior court’s conclusion that “the

Biological integrity standard is clear[,]” it could be clear only to the extent the

operative terms in the standard are defined. However, the superior court applied

“clear” definitions where the regulations simply do not provide definitions. The

superior court defined the biological integrity standard to mean that “DWR must

protect the indigenous community by determining reference conditions in terms of an

evaluated impacts on the community’s species composition, diversity, population

density and functional organization.” But this is not the standard as defined by the

applicable regulations. Again, classification is determined by “the existing or

contemplated best usage of the various streams and segments of streams in the basin,

as determined through studies and evaluations and the holding of public hearings for

consideration of the classifications proposed.” 15A N.C.A.C. 2B.0301 (2013)

(emphasis added). The North Carolina Administrative Code (“Code”) contemplates

the existing state of the water or its possible best usage. See id. The “Best Usage” of

Class C waters is “aquatic life propagation and maintenance of biological integrity

(including fishing and fish), wildlife, secondary recreation, agriculture, and any other

usage except for primary recreation or as a source of water supply for drinking,

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culinary, or food processing purposes[.]” 15A N.C.A.C. 2B.0211. “Conditions Related

to Best Usage” note “the waters shall be suitable for aquatic life propagation and

maintenance of biological integrity, wildlife, secondary recreation, and agriculture.

Sources of water pollution which preclude any of these uses on either a short-term or

long-term basis shall be considered to be violating a water quality standard.” Id.

(emphasis added).

The Code does not require the biological integrity of an aquatic ecosystem to

remain exactly or even substantially the same as it had once been, for example, prior

to discharge. See generally 15A N.C.A.C. 2B.0301. To violate a water quality

standard, the discharge of water must “preclude any of these uses on either a short-

term or long-term basis[.]” 15A N.C.A.C. 2B.0211. “Preclude” is not defined in the

statute, but its ordinary meaning is to “close” and “to make impossible by necessary

consequence: rule out in advance[.]” Merriam-Webster’s Collegiate Dictionary 977

(11th ed. 2003). In other words, to violate a water quality standard the discharge of

water must make “aquatic life propagation and maintenance of biological integrity,

wildlife, secondary recreation, and agriculture” nearly impossible. 15A N.C.A.C.

2B.0211; see generally Merriam-Webster’s Collegiate Dictionary 977.

Further, the superior court did not reverse the ALJ’s findings of fact as to

DEQ’s expertise applying the regulations which ultimately led to the contested

conclusion by the ALJ that DEQ had complied with the biological integrity standard:

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131. Mr. Reeder testified that with the assistance of DWR
staff, he used his best professional judgment, experience
and expertise to determine that the appropriate “aquatic
ecosystem” was the watershed system of Blounts Creek
and its tributaries. (Reeder, Tr. Vol. 7 pp. 1149-1150)

132. Mr. Reeder considered “reference conditions” to be
the existing conditions in the Blounts Creek aquatic
ecosystem without the proposed discharge. (Reeder, Tr.
Vol. 7 pp. 1142-1144, 1149-1150; Reeder, Tr. Vol. 4 pp. 662-
663; Fleek, Tr. Vol. 6 pp. 992-993)

....

136. Mr. Reeder took into consideration and weighed Mr.
Fleek’s opinions regarding the effects of the proposed
discharge on benthos in the upper reaches immediately
downstream of the proposed discharge outfalls. (Reeder,
Tr. Vol. 4 pp. 660-661)

137. Mr. Reeder understood Mr. Fleek’s professional
opinion to be that benthic macroinvertebrates would likely
become more diverse near the discharge outfalls and that
farther downstream any such impacts would lessen or
dissipate. (Reeder, Tr. Vol. 4 pp. 660-661)

138. Mr. Reeder also understood that the many other
tributaries of the Blounts Creek aquatic ecosystem, and the
biota inhabiting those areas, would be unaffected by the
permitted discharge. (Reeder, Tr. Vol. 7 pp. 1142-1151,
1162-1165, 1172; Reeder, Tr. Vol. 4 pp. 658-671; Ex. R23;
Ex. R1; Ex. R16)

Despite these findings of fact, Petitioners argued, and the Superior Court found, that

DEQ’s interpretation of the regulations and process for evaluation of the impact of

the proposed discharge were not “reasonable” and thus not subject to deference.

One of respondents’ main contentions before this Court is that the superior

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court failed to apply the correct legal standard in deferring to DEQ as to the

interpretation and application of the biological integrity standards. The superior

court determined “DWR failed to determine the base line metrics required by 15A

NCAC 02B.0202(11) and could not, therefore, ensure reasonable compliance with the

biological integrity standard,” but, according to Mr. Reeder, “no statutes or rules set

forth numeric standards or explicit methods or metrics by which DWR must make a

determination that a NPDES permit reasonably ensures compliance with the

biological integrity standard.” As DEQ explains,

the Superior Court’s “plain language” interpretation is not
based on the plain language of applicable regulations at all.
By stepping outside the plain language of the regulations
and dictating what information the agency’s biologists and
engineers must consider when evaluating compliance with
a technical environmental standard, the Superior Court
improperly substituted its judgment for that of the agency
. . . [, and]
....
As a pure question of regulatory interpretation, the
Superior Court’s “plain language” reading is flatly
incorrect. The “plain language” of the standard says
nothing about what process the agency must go through or
what information the agency must collect to reasonably
ensure compliance with the standard. Rather, the
regulations leave this determination to the “reasonabl[e]”
discretion of DWR’s environmental scientists to be
evaluated on a case-by-case basis. 15A NCAC 2H.0112(c).

The superior court considered a few lines of testimony of Mr. Reeder, “Tom

Reeder with DWR testified that he did not know if there was such a thing as a

biological integrity analysis; that he had never really heard of such a thing.” But this

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interpretation takes the testimony out of context and is not supported by the whole

record as noted by the next sentence in the order noting he further testified accurately

“that no statutes or rules set forth numeric standards or explicit methods or metrics

by which DWR must make a determination that a NPDES permit reasonably ensures

compliance with the biological integrity standard.” In fact, the superior court did not

determine that the ALJ’s findings regarding DEQ’s investigation of the expected

effects of the water discharge on biological integrity were not supported by the whole

record, but relied upon this statement by Mr. Reeder along with an erroneous

definition of “biological integrity” to conclude that

DWR staff conceded that the agency did not evaluate
species composition, diversity, population density, or
functional organization in Blounts Creek. Mr. Reeder
justified the failure to evaluate these metrics by saying
that he considered the impact of the permitted discharge to
be de minimus. In essence the agency reached the ultimate
conclusion that the impact of the permitted discharge was
de minimus first, without evaluating species composition,
diversity, population density, and functional organization,
and then used the ultimate conclusion to conclude that
evaluation of the metrics was unnecessary.

But DEQ certainly did not “concede[]” that it “did not evaluate specifies

composition, diversity, population density, or functional organization[]” despite the

portions of Mr. Reeder’s testimony the superior court and Petitioners take out of

context. DEQ simply did not perform evaluations to Petitioners’ desired

specifications, but this is vastly different from failing to evaluate at all. The question

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for the superior court, and for this Court, is not whether DEQ could have done more

or different testing or analysis or whether the ALJ could have found different facts.

The questions before us are whether the ALJ’s findings of fact are supported by the

whole record; N. Carolina Dep’t of Pub. Safety, 247 N.C. App. at 286, 786 S.E.2d at

64; whether DEQ evaluated the Permit application in accord with the applicable

regulations; and whether DEQ’s interpretation of those regulations was reasonable.

See Hilliard v. N.C. Dep’t of Corr., 173 N.C. App. 594, 598, 620 S.E.2d 14, 17 (2005)

(“On judicial review, an agency’s interpretation of its own regulations will be enforced

unless clearly erroneous or inconsistent with the regulation’s plain language.”); see

generally N. Carolina Dep’t of Pub. Safety v. Ledford, 247 N.C. App. 266, 286–87, 786

S.E.2d 50, 63–64 (2016) (“[O]ur Supreme Court has made clear that even under our

de novo standard, a court reviewing a question of law in a contested case is without

authority to make new findings of fact. Under the whole record test, the reviewing

court may not substitute its judgment for the ALJ’s as between two conflicting views,

even though it could reasonably have reached a different result had it reviewed the

matter de novo. Instead, we must examine all the record evidence—that which

detracts from the ALJ’s findings and conclusions as well as that which tends to

support them—to determine whether there is substantial evidence to justify the

ALJ’s decision. Substantial evidence is relevant evidence a reasonable mind might

accept as adequate to support a conclusion. We undertake this review with a high

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degree of deference because it is well established that in an administrative proceeding,

it is the prerogative and duty of the ALJ, once all the evidence has been presented

and considered, to determine the weight and sufficiency of the evidence and the

credibility of the witnesses, to draw inferences from the facts, and to appraise

conflicting and circumstantial evidence. The credibility of witnesses and the probative

value of particular testimony are for the ALJ to determine, and the ALJ may accept or

reject in whole or part the testimony of any witness.” (emphasis added)).

The whole record supports the ALJ’s findings that DEQ evaluated species

composition, diversity, population density, and functional organization in accord with

its established procedures and expertise. Mr. Reeder was “the acting director of the

Division of Water Quality and the director of the Division of Water Resources” when

the Permit was approved; eventually the two divisions were merged. Mr. Reeder

approved the Permit, but he was by no means the only employee of DEQ involved in

the consideration of the Permit. Many employees of DEQ, as well as consultants

including CZR Incorporated (“CZR”) and Kimley-Horn and Associates (“Kimley

Horn”), performed the actual sampling and analysis of water quality, fish, and

benthos in Blounts Creek. Mr. Reeder testified at length regarding DEQ’s

investigation and analysis of “biological integrity” in Blount’s Creek. As a whole, in

context, Mr. Reeder testified “biological integrity” is a narrative standard, not a

numeric standard:

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Well, I mean you can’t go to an [Standard Operating
Procedure]—there’s no [Standard Operating Procedure]
that says biological integrity analysis. Like I couldn’t call
Eric Fleek on the phone and say, “Hey, Eric, go out and do
a biological integrity analysis.”
What you do is you go out and do exactly what Eric
did, is you do a biological assessment and you look at the
technical memorandum, and according to that you make a
decision based upon your best professional judgment and
all the data as to whether you think this narrative
standard for biological integrity will be violated or not.

Mr. Eric Fleek was an environmental supervisor at DEQ. Mr. Fleek testified his

branch, the Biological Assessment Branch, evaluated water quality by “sampling for

fish. We also do sampling for benthic macroinvertebrates. And by assessing a water

body and the biology that lives there, you can use them as proxies to determine what

the water quality is like there.” Mr. Fleek also testified that there were “protocols for

doing that sampling” of Blounts Creek in reference to the Standard Operating

Procedure.

Our record contains one of Petitioners’ exhibits in arguing DEQ failed to

comply with its own standards, DEQ’s “STANDARD OPERATING PROCEDURE

BIOLOGICAL MONITORING[,] STREAM FISH COMMUNITY ASSESSMENT

PROGRAM[,]” (“Standard Operating Procedures”) and

the purpose of this manual [is] to provide details on
standard operating procedures of the Biological
Assessment Unit of the Division of Water Quality (DWQ or
Division) for the collection and analysis of stream fish
community assessment data. Consistency in data
collection and analysis is the cornerstone for evaluating

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biological integrity. The procedures provided are a
synthesis of widely used methods and methods developed
from the experience of personnel within the Unit. These
methods have been shown to provide repeatable and useful
data for water quality evaluation.
....
The Stream Fish Community Assessment Program
was designed as an additional basinwide assessment tool
and has been in existence since 1991. It’s core mission is
to sample a set of fixed sites on lower Strahler order
wadeable creeks, streams, and rivers on a five-year
rotating basis to support the DWQ’s Basinwide
Management Plan Program.

While the Standard Operating Procedures address “biological integrity[,]” they

do not require a particular type of analysis to be done for a Permit application;

instead, the staff of DEQ uses its expertise to determine what types of testing or

sampling need to be done for each application, depending upon its unique

circumstances.

The Standard Operating Procedures also describe the “NORTH CAROLINA

INDEX OF BIOTIC INTEGRITY” which has been in use since the early 1990s:

The Division has been monitoring the biological integrity
of stream fish communities since the early 1990s. The
biological monitoring tool that is used is referred to as the
North Carolina Index of Biological Integrity (NCIBI). The
NCIBI method was developed for assessing a stream’s
biological integrity by examining the structure and health
of its fish community. The North Carolina Administrative
Code defines Biological Integrity as: “. . . the ability of an
aquatic ecosystem to support and maintain a balanced and
indigenous community of organisms having species
composition, diversity, population densities, and functional
organization similar to that of reference conditions” (15A

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NCAC 02B .0200; NCAC 2004). The NCIBI is a
modification of the Index of Biotic Integrity (IBI) initially
proposed by Karr (1981) and Karr, et al. (1986).

The NCIBI incorporates information about species
richness and composition, trophic composition, fish
abundance, and fish condition. The NCIBI summarizes the
effects of all classes of factors influencing aquatic faunal
communities such as water quality, energy source, habitat
quality, flow regime, and biotic interactions. While any
change in a fish community can be caused by many factors,
certain aspects of the community are generally more
responsive to specific influences. Species composition
measurements reflect habitat quality effects. Information
on trophic composition reflects the effect of biotic
interactions and energy supply. Fish abundance and
condition information indicates additional water quality
effects. It should be noted, however, that these responses
may overlap. For example, a change in fish abundance may
be due to decreased energy supply or a decline in habitat
quality, not necessarily a change in water quality.

The scores derived from this index are a measure of the
ecological health of the waterbody and may not directly
correlate to water quality. For example, a stream with
excellent water quality, but with poor or fair fish habitat,
may not be rated excellent with this index. However, a
stream which rated excellent on the NCIBI should be
expected to have excellent water quality.

Further, the NCIBI sets out specific metrics to assess biological integrity:

The NCIBI incorporates information about species
richness and composition, pollution indicator species,
trophic composition, fish abundance, fish condition, and
reproductive function by the cumulative assessment of 12
parameters or metrics (Tables 1-3). Each metric is
designed to contribute unique information to the overall
assessment. The values provided by the metrics are
converted into scores on a 1, 3, and 5 scale. A score of 5

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represents conditions commonly associated with
undisturbed reference streams in the specific river basin or
ecoregion. A score of 1, however, indicates that conditions
deviate greatly from those typically observed in
undisturbed streams of the region. All metrics for each of
the three regions were calibrated using regional reference
sites.

The scores for all metrics are then summed to obtain the
overall NCIBI score, an even number between 12 and 60.
The score is then used to determine the biological integrity
class of the stream (i.e., Poor, Fair, Good-Fair, Good, or
Excellent) (Karr 1981 , Karr, et al. 1986). A fish community
rated Excellent is comparable to the best situations with
minimal human disturbance; all regionally expected
species for the habitat and stream size, including the most
intolerant forms, are present along with a full array of size
classes and a balanced trophic structure. Conversely, a
fish community rated Poor deviates greatly from the
reference condition. The number of fish is fewer than
expected, usually fewer than expected number of species,
an absence of intolerant species, and an altered trophic
structure. Communities rated Good, Good-Fair, or Fair fall
within this disturbance gradient.

Currently, if a fish community is rated Excellent, Good, or
Good-Fair it is deemed to be Fully Supporting its Aquatic
Life Use Support stream classification. If a fish community
is rated Fair or Poor it is deemed to be Not Supporting its
Life Use Support stream classification and the water
quality standard is not being met. Waters that have an
Excellent fish community rating are also eligible for
reclassification to a[n] Outstanding Resource Waters or to
a High Quality Waters supplemental classifications.

The Standard Operating Procedures set forth twelve metrics, grouped into five

categories:

1. Species richness and composition (Metric Nos. 1 and

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3-5)
2. Indicator species (Metric Nos. 6 and 7)
3. Trophic function (Metric Nos. 8-10)
4. Abundance and condition (Metric Nos. 2 and 11)
5. Reproductive function (Metric No. 12)

The particular metrics used may vary depending upon the type of water and region

of the state. For example, the species of fish measured metric number 4 are different

in mountain streams than in and around coastal waters. The Standard Operating

Procedures also set out sampling procedures and instructions for laboratory

processing for samples. To assess the quality of a stream, information obtained from

sampling is compared to reference conditions. “The scores for all 10 or 12 metrics are

then summed to obtain the overall NCIBI score. Finally, the score (an even number

between 12 and 60) is then used to determine the biological integrity class of the

stream from which the sample was collected[.]”

Regarding permits, the Standard Operating Procedures provide, “The location

of permitted dischargers should be reviewed, using the database provided by the

Division’s Basinwide Information Management System” and notes that “[w]atershed-

specific special study sites that are designed to address a specific, short-term question

(e.g., Use Attainability, impacts from a permitted discharger, watershed

modifications, etc.) are usually sampled only once and may be sampled anytime

between March and December.” (Emphasis added.)

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As part of its analysis of the permit application, CZR did sampling and

prepared a report addressing the metrics noted in the Standard Operating

Procedures regarding fish and benthos. This report noted that fish surveying was

done “in accordance with NCDWQ 2006 Standard Operating Procedure, Stream Fish

Community Assessment Program (NCDENR 2006a).” “Benthic invertebrate

sampling occurred on 11 April 2011 following the swamp stream method as described

in NCDWQ 2006 Standard Operating Procedures for collection of benthic

invertebrates in the Level IV Ecoregion Swamp Region B of the coastal plain of North

Carolina NCDENR 2006b.”

DEQ initially reviewed Martin Marietta’s application for the Permit, then

requested additional information to address several questions:

1. Please define a zone of impact (ZOI) and show that
it is not degraded, considering hydraulic, biota, & saline
water impacts as discussed below.
Hydraulic: The point downstream at which the
proposed discharge can be considered insignificant.
Consider the frequency of bank overflow and the
effects of increased water levels, velocity changes,
and erosion. Impacts should be based on a major
rainfall event such as an 80th percentile (two in 10-
year) storm, and a base flow.
Biota: The point at which the proposed discharge is
considered to be insignificant, relative to
anadromous fish (e.g. finfish) changes in velocity,
pH, temperature DO. Evaluate effects during
documented spawning times (as per the NC Wildlife
Resources Commission and the National Marine
Fisheries Service) and during periods of lower
stream flows.

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Saline Water: The point at which the
freshwater impact of the proposed discharge is
considered insignificant. Using the ZOI identified
for the hydraulic component, determine the distance
to a downstream point of saline stability and
evaluate impacts
2. Please provide a process flow diagram for the mine
dewatering and stormwater discharge, including the flow
around the proposed stockpile area. What is the
approximate size and capacity of the settling pond that will
be located next to the mining pit?
3. What is the size and capacity of the closed loop
settling system and the future overburden storage area?
4. Please provide an expanded Engineering
Alternatives Analysis (EAA). This should include the
alternatives of reinjection of pit drainage and the
treatment and conveyance of this discharge for potable or
other reusable purposes. The EAA must be performed
according to the guidelines in the Division’s website. This
includes a 20-year present worth analysis of all feasible
options.

In answer to these questions, Martin Marietta provided a Technical

Memorandum prepared by Kimley Horn summarizing “the results of several analyses

performed to address comments regarding stream stability, potential flooding, and

water quality issues associated with the proposed discharge[,]” including “the

predicted zones of potential impact[;]” a revised NPDES Water Flow Map showing

“the process flow diagram for mine dewatering and stormwater discharge[;] and

“expanded Engineering Alternatives Analysis (EAA) dated September 14, 2012,

prepared by Groundwater Management Associates, Inc. . . . according to the

guidelines in the DWQ website and includ[ing] a 20-year present worth analysis of

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all feasible options.” Further, in October of 2012, CZR also prepared a Technical

Memorandum addressing “potential direct and indirect effects on identified fish

populations from predicted changes in Blounts Creek water quality as identified by”

Kimley Horn’s Technical Memorandum.

In summary, hundreds of pages of the record on appeal and hundreds of pages

of testimony address the analysis of “biological integrity,” as well as salinity, pH, and

many other factors evaluated by DEQ to determine whether the Permit should be

issued. To the extent that the superior court made a finding of fact in noting that

Tom Reeder with DWR testified that he did not
know if there was such a thing as a biological integrity
analysis; that he had never really heard of such a thing.
He further testified that no statutes or rules set forth
numeric standards or explicit methods or metrics by which
DWR must make a determination that a NPDES permit
reasonably ensures compliance with the biological
integrity standard[,]

this finding is technically supported by the record because Mr. Reeder did so testify.

But neither the superior court nor this Court may substitute its findings of fact for

those of the ALJ; we review the ALJ’s findings of fact only to determine if they are

supported by the whole record. See Ledford, 247 N.C. App. at 286–87, 786 S.E.2d at

63–64. The ALJ’s findings are supported by the whole record, as discussed above.

Contrary to the superior court’s conclusions, Mr. Reeder’s testimony indicated the

thorough and extensive evaluation that DEQ undertook to ensure biological integrity,

although this cannot be neatly summed up as one official analysis plainly laid out in

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a specific standard operating procedure. The ALJ’s findings as to the biological

integrity analysis are supported by the whole record. The superior court therefore

erred by essentially substituting its own findings of fact regarding Mr. Reeder’s

testimony and by making legal conclusions as to biological integrity based upon a

misinterpretation of the standard. Therefore, as to DEQ’s and Martin Marietta’s

main contention on appeal we agree that the trial court erred in reversing the ALJ’s

order as to the biological standard, and we now turn to address Petitioners’ issues on

cross-appeal.

D. Swamp Waters Classification

Petitioners cross-appealed from the superior court’s order based upon its

determination that DEQ’s approval of the Permit violated the water quality

standards set forth for swamp water classification. DEQ and Martin Marietta argue

we should affirm the findings and conclusions of the ALJ and superior court regarding

swamp waters. As noted above, a body of water may have a supplemental

classification in addition to its primary classification. See generally 15A N.C. Admin.

Code 2B.0301. The portions of Blounts Creek at issue have a supplemental

classification of “swamp waters” which again is defined as “those waters which are

classified by the Environmental Management Commission and which are

topographically located so as to generally have very low velocities and other

characteristics which are different from adjacent streams draining steeper

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topography.” 15A N.C.A.C. 2B.0202. Swamp water classification applies to “waters

which have low velocities and other natural characteristics which are different from

adjacent streams.” 15A N.C.A.C. 2B.0101.

The ALJ identified the issue regarding swamp waters as follows:

Issue 2: “Swamp Waters Claim”: Whether Petitioners
have met their burden of proving that Respondent
exceeded its authority or jurisdiction, acted erroneously,
failed to use proper procedure, acted arbitrarily or
capriciously, or failed to act as required by law or rule in
determining the NPDES Permit reasonably ensures
compliance with water quality standards and regulations
related to the “Swamp Waters” supplemental
classification.

The ALJ made the following findings regarding the swamp water

classification:

18. Contrary to Petitioners’ assertions, the evidence
demonstrates that the “swamp method” and the term
“swamp stream” in the SOP are unrelated to the “swamp
waters” supplemental classification. (Fleek, Tr. Vol. 7 pp.
1103-1105; Ex. R34, p.6; Fleek, Tr. Vol. 6 pp. 980-981; Ex.
P58; Ex. P59)

19. Mr. Fleek reviewed the CZR Habitat Assessment
and provided input to Mr. Belnick. In Mr. Fleek’s
evaluation, he concluded that there could be an increase in
diversity and population of benthos near the proposed
discharge outfalls because the discharge would lead to less
stressful conditions. (Fleek, Tr. Vol. 7 pp. 1108-1111, 1114-
1116; Ex.R4; Ex. 51)

....

Petitioners’ Swamp Waters Claim

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81. Petitioners claim that the NPDES Permit does not
reasonably ensure compliance with what Petitioners
characterize as a requirement to “protect” swamp waters
“characteristics.” Petition 4-5.

82. “Swamp Waters” are defined as “waters which are
classified by the Environmental Management Commission
and which are topographically located so as to generally
have very low velocities and other characteristics which are
different from adjacent streams draining steeper
topography.” 15A NCAC 02B.0202(62). See also 15A
NCAC 02B.0101(e)(2) and 02B .0301(c).

83. Petitioners claim that DWR has a duty to preserve
swamp waters in their existing condition, and they objected
to the predicted changes in physical and chemical
parameters in upper Blounts Creek, specifically dissolved
oxygen, pH, flow velocity, and tannins. Petitioners have
characterized the predicted changes to these parameters as
unlawfully eliminating swamp waters characteristics and
uses.

84. DWR disagrees with Petitioners in that DWR has a
duty under the applicable rules and laws to preserve
waters with the supplemental classification “swamp
waters” in their existing condition. DWR asserts,
consistent with its longstanding interpretation and past
practices, that the only effect of the Sw supplemental
classification is to modify the water quality standards for
dissolved oxygen and pH by lowering the minimum limits
otherwise required for Class “C” waters. See 15A NCAC
02B .0211(3)(b) and (3)(g) (2013).

85. Petitioners failed to identify any statute or rule that
expressly protects “low tannins”, “low pH”, “low dissolved
oxygen”, or “low velocity” attributes of swamp waters.

86. Petitioners have not cited a law or rule that requires
additional protection or use for waters with the

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supplemental classification “swamp waters.”

87. The swamp waters supplemental classification and
the water quality standards administered by DWR relate
to a highly technical and scientific subject area within
DWR’s expertise.

88. As the agency delegated the responsibility for
NPDES permitting and enforcement of North Carolina’s
water quality standards, DWR’s interpretation and
application of the State’s water quality standards, and its
surface water classifications and supplemental
classifications are entitled to deference. Hilliard v. N.C.
Dept. of Corrections, 173 N.C. App. 594, 598, 620 S.E.2d
14, 17-18 (2005).

89. DWR’s interpretation and application of the highly
technical rules it administers, including the swamp waters
and antidegradation rules, are reasonable, longstanding,
in accord with past DWR practices, and consistent with and
supported by the plain language of the relevant rules.

90. Petitioners have presented no evidence, authority,
or argument that persuades the undersigned to overrule
DWR’s rational interpretation and application of the
State’s swamp waters and antidegradation laws and rules.

91. Some supplemental classifications may trigger
protection or uses in addition to the protections or uses for
Class C waters. For example, the “Outstanding Resource
Waters” supplemental classification states that such
waters “require special protection to maintain existing
uses.” 15A NCAC 02B .0101(e)(4).

92. The specificity of additional protections and uses
explicitly applicable by rule to some supplemental
classifications is further evidence that, if the “swamp
waters” supplemental classification was intended to
provide additional protections, the rules would have
specifically provided for such protections. See, e.g.,

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Mangum v. Raleigh Bd. Of Adjustment, 196 N.C. App. 249,
255, 674 S.E.2d 742, 747 (2009) (“One of the longstanding
rules of interpretation and construction in this state is
expressio unius est exclusio alterius, the expression of one
thing is the exclusion of another.”) (citations omitted).

93. The term “swamp waters” is a regulatory term that
guides the assignment of the Sw supplemental
classification to particular stream segments; and once the
assignment is made by rule, the only regulatory effect of
the assignment of the swamp waters supplemental
classification is to lower the acceptable minimum values
for pH and dissolved oxygen. See 15A NCAC 02B
.0211(3)(b) and (3)(g) (2013). Upper Blounts Creek, for
example, has been assigned the “Sw” supplemental
classification by formal rulemaking. 15A NCAC 02B
.0316(a) (Index Number 29-9-1-(1)).

94. Petitioners’ arguments that DWR misinterpreted
and misapplied the swamp waters supplemental
classification present questions of law and fact, and mixed
questions of law and fact. Petitioners’ arguments have
been thoroughly considered and rejected by the
undersigned as unpersuasive and unsupported by the
preponderance of evidence.

95. Petitioners rely on a sentence from the State’s
antidegradation policy: “Existing uses, as defined by Rule
.0202 of this Section, and the water quality to protect such
uses shall be protected by properly classifying surface
waters and having standards sufficient to protect these
uses.” 15A NCAC 02B .0201(b). See Petition at 4-5.

96. According to its plain language, this provision is
implemented by formal rulemaking that establishes
classifications, uses and water quality standards, and that
assign classifications, uses and standards to individual
surface water segments. See, e.g., 15A NCAC 02B .0211
(2013) (uses and standards for Class C waters, including
waters with the supplemental “Sw” classification), 15A

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NCAC 02B .0316(a) (Index Number 29-9-1-(1) (assignment
of classifications to upper Blounts Creek).

97. There are antidegradation permitting procedures
that did apply to DWR’s evaluation and issuance of the
NPDES Permit, but Petitioners have not argued that these
applicable procedures were not followed.

98. The preponderance of the evidence demonstrates
that DWR reasonably interpreted the laws and rules
governing swamp waters and the state’s antidegradation
policy, and reasonably applied those laws and rules to the
data, studies, and other information submitted or obtained
during the course of DWR’s NPDES permitting review and
decision.

99. Petitioners failed to present evidence sufficient to
overcome the presumption that DWR acted appropriately
in determining the NPDES Permit reasonably ensures
compliance with water quality standards or regulations
related to the “Swamp Waters” supplemental
classification.

100. Petitioners failed to meet their burden of proving by
a preponderance of the evidence that DWR exceeded its
authority or jurisdiction, acted erroneously, failed to use
proper procedure, acted arbitrarily or capriciously, or failed
to act as required by law or rule in determining that the
laws and rules do not require protection of the existing
conditions or characteristics of surface waters with the
supplemental classification “swamp waters” and that the
NPDES Permit reasonably ensures compliance with water
quality standards and rules related to the “Swamp Waters”
supplemental classification.

101. DWR’s decision that the NPDES Permit reasonably
ensures compliance with all applicable water quality
standards and rules, including those relating to the swamp
waters supplemental classification, is affirmed.

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....

110. Petitioners failed to present evidence sufficient to
overcome the presumption that DWR acted appropriately
in issuing the Permit.

111. Petitioners failed to meet their burden of proving
Respondent DWR exceeded its authority or jurisdiction,
acted erroneously, acted arbitrarily and capriciously, used
improper procedure, or failed to act as required by law or
rule in issuing the NPDES Permit.

112. DWR’s issuance of the NPDES Permit is affirmed in
all respects.

....

119. Petitioners contend that the NPDES Permit is
unlawful because the Permit does not reasonably ensure
compliance with what Petitioners characterize as a
requirement to “protect” swamp waters “characteristics,”
which they contend include “low velocity,” “low dissolved
oxygen,” “low pH,” and “high tannins.” (Petition 4-5)

120. “Swamp Waters” are defined as “waters which are
classified by the Environmental Management Commission
and which are topographically located so as to generally
have very low velocities and other characteristics which are
different from adjacent streams draining steeper
topography.” 15A NCAC 2B.0202(62). See also 15A NCAC
2B .0101(e)(2) and 2B .0301(c).

121. The “swamp waters” supplemental classification
modifies the water quality standards for dissolved oxygen
and pH in the upper Blounts Creek segment by lowering
the minimum pH and dissolved oxygen values otherwise
required for Class “C” waters:

(b) Dissolved oxygen: . . . for non-trout waters, not
less than a daily average of 5.0 mg/1 with a

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minimum instantaneous value of not less than 4.0
mg/1; swamp waters, lake coves or backwaters, and
lake bottom waters may have lower values if caused
by natural conditions;

....

(g) pH: shall be normal for the waters in the
area, which generally shall range between 6.0 and
9.0 except that swamp waters may have a pH as low
as 4.3 if it is the result of natural conditions[.]

15A NCAC 2B .0211(3)(b), (g) (2013)

122. Under DWR’s longstanding interpretation of the
statutes and rules that it administers, the supplemental
classification of swamp waters does not provide any
additional protections to water bodies to which it is
assigned; and low flow and velocity, low pH, low dissolved
oxygen, and high tannins are not uses, standards,
characteristics, or parameters of swamp waters that are
required to be maintained or protected. (Reeder, Tr. Vol. 7
pp. 1154-1157; Reeder, Tr. Vol. 4 pp. 653-657; Belnick, Tr.
Vol. 4 pp. 523-524, 557-558; Reeder, Tr. Vol. 4 pp. 653-657;
Belnick, Tr. Vol. 6 pp. 1059-1060)

123. The CZR report states that with the proposed
discharge, upper Blounts Creek may no longer exhibit
intermittent flow, low dissolved oxygen concentrations,
and high tannins. (Ex. R16 p. 10)

124. The report also states that, with the proposed
discharge, the use of the swamp stream sampling method
may no longer be appropriate to evaluate benthic
macroinvertebrates. (Ex. R16 p. 10)

125. The report does not state that the swamp waters
supplemental classification requires the preservation or
maintenance of low dissolved oxygen, high tannins, low
velocities, and low pH as contended by Petitioners. (Ex.

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R16 p. 10)

126. Based on the evidence before it, DWR concluded that
the Permit reasonably ensures compliance with all
applicable water quality standards, including those
applicable to upper Blounts Creek, which has a C primary
classification and a Sw supplemental classification.

(Alterations in original.)

The superior court affirmed the ALJ’s final decision as to the swamp water

classification issue. The superior court stated the issue as follows

II. Did the ALJ err in upholding DWR’s issuance of the
Permit as reasonably ensuring compliance with:

A. The swamp waters supplemental
classification and antidegradation rule[.]

The superior court addressed Petitioners’ swamp water claim as follows:

North Carolina’s water quality regulations protect
North Carolina’s surface waters by: (1)

[Text truncated at 120,000 characters. The full text is on the page linked above.]

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Source: Frix Law Library, https://www.frixlaw.com/law-library/cases/10485872. Public record. Not legal advice.
