The opinion
MAINE SUPREME JUDICIAL COURT Reporter of Decisions
Decision: 2025 ME 35
Docket: Ken-23-348
Argued: April 10, 2024
Decided: April 10, 2025
Panel: STANFILL, C.J., and MEAD, HORTON, CONNORS, LAWRENCE, and DOUGLAS, JJ.
EASTERN MAINE CONSERVATION INITIATIVE et al.
v.
BOARD OF ENVIRONMENTAL PROTECTION
DOUGLAS, J.
[¶1] Eastern Maine Conservation Initiative and Roque Island Gardner
Homestead Corporation (collectively, “Petitioners”) appeal from a judgment of
the Superior Court (Kennebec County, Murphy, J.) affirming the Board of
Environmental Protection’s decision upholding a permit issued by the
Department of Environmental Protection to Kingfish Maine, Inc. for an
aquaculture operation in Jonesport. The permit, which the Department issued
after conditionally granting Kingfish a wastewater discharge permit for the
same project, authorized Kingfish to construct a facility in accordance with the
Site Location of Development Law (Site Law), 38 M.R.S. §§ 481 to 489-E (2024),
and to install intake and outfall pipes pursuant to the requirements of the
Natural Resources Protection Act (NRPA), 38 M.R.S. §§ 480-A to 480-JJ (2024).
2
Petitioners argue that the Board erred in determining the scope of its review
under NRPA and by approving the NRPA component of the permit without
independently evaluating the environmental impacts associated with the
discharge of treated wastewater. We disagree and affirm the judgment.
I. BACKGROUND
[¶2] The following facts and procedure are derived from the Board’s
supported findings and the procedural record. See Sultan Corp. v. Dep’t of Env’t
Prot., 2022 ME 21, ¶ 2, 272 A.3d 296; Martin v. MacMahan, 2021 ME 62, ¶ 2, 264
A.3d 1224.
[¶3] In 2020, Kingfish began the process of securing permits from the
Department to construct and operate a land-based recirculating aquaculture
system designed to raise saltwater fish. The project involves the construction
of a facility consisting of two primary buildings, access roads, and ancillary
buildings. It also involves the installation of two approximately 1,400-foot-long
intake pipes to draw water from Chandler Bay and two approximately
2,800-foot-long outfall pipes to discharge treated wastewater into the bay.
Kingfish proposed to begin construction of the facility and the pipes upon
obtaining all required federal, state, and local permits.
3
A. Agency Proceedings
1. The Discharge Permit
[¶4] In August 2020, Kingfish applied to the Department for a combined
Maine Pollutant Discharge Elimination System Permit and Water Discharge
License (the discharge permit) to allow for a daily maximum discharge of 28.7
million gallons of treated wastewater from the proposed aquaculture facility.
See 38 M.R.S. § 413 (2024).
[¶5] In June 2021, the Department approved Kingfish’s application and
issued the discharge permit. The Department found that the effluent discharge
from the facility into Chandler Bay would not lower the quality of any classified
body of water below its stated classification or the quality of any unclassified
body of water below its anticipated classification.1 See 38 M.R.S.
§ 414-A(1)(A), (B) (2024); 38 M.R.S. § 465-B(2) (2020)2. In addition, the
Chandler Bay is a Class SB body of water, the “2nd highest classi ication.” 38 M.R.S. § 465-B(2)
1
(2020). Petitioners do not dispute this fact.
2 Section 465-B(2) has recently been amended. See P.L. 2021, ch. 551, § 15 (effective Aug. 8, 2022)
(codi ied at 38 M.R.S. § 465-B(2)(B) (2024)); see also infra n.14. Because this amendment took effect
after King ish’s discharge permit application became complete on August 17, 2020, we cite to the
2020 Maine Revised Statutes, which contain the version of section 465-B(2) that was effective on that
date. See 06-096 C.M.R. ch. 2, § 11(F) (effective June 9, 2018) (“Unless otherwise provided by law, all
license applications . . . are subject to the substantive laws and rules in effect on the date the
application is accepted as complete for processing.”).
Several other statutes referenced in this opinion have also been amended recently. See, e.g., P.L.
2023, ch. 481, § 11 (effective Oct. 25, 2023) (codi ied at 38 M.R.S. § 480-D(1) (2024)); P.L. 2021, ch.
551, § 7 (effective Aug. 8, 2022) (codi ied at 38 M.R.S. § 464(4)(F)(2) (2024)). In each of these other
4
Department found that the effluent discharge associated with Kingfish’s project
would satisfy various applicable licensing standards, including dilution criteria,
06-096 C.M.R. ch. 530, §§ 2-4 (effective Mar. 21, 2012), dissolved oxygen
criteria, 38 M.R.S. § 465-B(2)(B), and temperature criteria, 06-096 C.M.R.
ch. 582 (effective May 4, 1996). But the Department found that the effluent
discharge would exceed the default threshold for levels of nitrogen
concentration and would therefore lower water quality3 specifically in relation
to eelgrass habitat.4 The Department explained, however, that its finding of an
anticipated lowering of water quality “is not a determination that there is
toxicity related to the discharge nor . . . a determination that the discharge is in
violation of any water quality criterion or standard. Rather, this determination
triggers the [State’s] antidegradation process in 38 M.R.S. § 464(4)(F)(5).”5 The
instances, we cite the 2024 Maine Revised Statutes because the amendments do not concern the
issues on appeal.
3 A lowering of “the existing quality of any body of water,” 38 M.R.S. § 414-A(1)(C) (2024), is
statutorily distinct from a lowering of “the quality of any classi ied body of water below such
classi ication,” 38 M.R.S. § 414-A(1)(A).
4 Without a uniform state or federal threshold for nitrogen concentration, the Department
employed a concentration threshold that was consistent with its historical practice and that took into
account the proximity of eelgrass to the discharge location.
5 The State’s antidegradation process enables the Department to approve a discharge permit even
if the proposed discharge is found to lower water quality. 38 M.R.S. § 464(4)(F); 38 M.R.S.
§ 414-A(1)(C). For a proposed discharge to qualify for a permit under this policy, the Department
must ind, following an opportunity for public participation, that the discharge is, among other
criteria, “necessary to achieve important economic or social bene its to the State” and that the water
body’s classi ication standard is either satis ied or, if it is not satis ied, that this de iciency is not
5
Department further found that the existing in-stream use of Chandler Bay by
the surrounding species and habitat would be maintained and protected.
See 38 M.R.S. § 464(4)(F)(1-A) (2024).
[¶6] The discharge permit imposes a number of standard and special
conditions, including numeric and narrative effluent limitations as well as
monitoring requirements. The narrative effluent limitations provide, in part,
that Kingfish “must not discharge effluent that contains materials in
concentrations or combinations which are hazardous or toxic to aquatic life”
and “must not discharge effluent that lowers the quality of any classified body
of water below such classification.” In addition, Kingfish is subject to ongoing
monitoring requirements whereby it must regularly measure and report on
water quality, including specifically the nitrogen concentration. The discharge
permit expressly provides that the Department may “modify this permit” to
require different effluent limits “where there is a reasonable potential that the
attributable to the proposed discharge. 38 M.R.S. § 464(4)(F)(3), (5). In applying the policy, the
Department can refer on a case-by-case basis to considerations in its non-binding Antidegradation
Waste Discharge Program Guidance. See Waste Discharge Program Guidance Memorandum from
Brian Kavanah, Director, Div. of Water Res. Regul., to Water Licensing & Compliance Staff (June 13,
2001), https://www.maine.gov/dep/bep/2021/12-16-21/TR%20AppB1_MDEP_WW-DEPLW0267
%20-%20antidegradation.pdf [https://perma.cc/T3H2-YSLF]. Such considerations include the
project’s potential to generate commercial activity, the applicant’s ability to comply with ef luent
limitations, the treatment facility’s maintenance, and the feasibility of alternative measures to
mitigate the diminution in water quality. Id.
6
effluent may cause water quality criteria to be exceeded” or to “change
monitoring requirements or limitations based on new information.”
[¶7] Petitioners did not appeal the Department’s decision to
conditionally approve Kingfish’s application for the discharge permit. Another
interested party, Sierra Club, did appeal the decision, but the Board dismissed
the appeal for lack of standing and for failing to comply with the Board’s
content-related requirements for appeals.
2. The NRPA and Site Law Permits
[¶8] In March 2021, Kingfish applied to the Department for a Site Law
permit to construct the facility, and also applied for a NRPA permit to install the
intake and outfall pipes. A NRPA permit was required because of the potential
impacts to freshwater and coastal wetlands from the construction and dredging
activities necessary for the pipes to be installed. See 38 M.R.S.
§ 480-C(2)(A), (D).
[¶9] On November 12, 2021, the Department approved Kingfish’s
application and issued a combined NRPA and Site Law permit with conditions.
With respect to the NRPA permit, Kingfish’s application satisfied the eleven
standards set out in the NRPA statute at 38 M.R.S. § 480-D, including the
standard relevant in this appeal, with the Department finding that
7
[t]he proposed activity will not unreasonably harm any significant
wildlife habitat, freshwater wetland plant habitat, threatened or
endangered plant habitat, aquatic habitat, travel corridor,
freshwater, estuarine, or marine fisheries or other aquatic life
provided that the applicant meets the requirements of Findings 6
and 16.6
See 38 M.R.S. § 480-D(3).
[¶10] Petitioners timely appealed to the Board.7
3. Petitioners’ Appeal to the Board
[¶11] In their written appeal to the Board, Petitioners, in making several
arguments, expressed broad concerns about the negative effects of the project
on the environment and fishing industries and specific concerns about the
effects of effluent on water quality, eelgrass, and other species. They also
asserted that the Department did not receive sufficient data to support its
issuance of the NRPA and Site Law permits and requested a public hearing
before the Board.
6 In the section of its decision referred to as “Finding 6,” the Department found that the pipeline
installation would not unreasonably harm neighboring wildlife and isheries. Speci ically, based on
the separately conducted reviews of the Maine Department of Inland Fisheries and Wildlife and the
Maine Department of Marine Resources, the Department found that the pipeline construction would
not signi icantly impact nearby wildlife, such as butter ly, lobster, and scallop populations. Similarly,
in the section referred to as “Finding 16,” the Department found that King ish’s proposal would
minimize anticipated alterations to freshwater and coastal wetlands and ensure adequate measures
to monitor wetland impacts and compensate for negative impacts where necessary.
7 Although Sierra Club also appealed the issuance of the combined NRPA and Site Law permit to
the Board, it is not a party to the present appeal.
8
[¶12] On August 4, 2022, the Board held a two-hour meeting at which it
heard presentations from Petitioners, Sierra Club, Kingfish, and the
Department. Petitioners renewed their request for a public hearing.
[¶13] Following the presentations, the Board voted on two items. First,
it voted to deny Petitioners’ request for a public hearing for two reasons—
because the record created before the Department was sufficient for the Board
to make a decision and because Petitioners did not provide a satisfactory offer
of proof as to what additional evidence they would present.8 See 06-096 C.M.R.
ch. 2, § 24(A), (B)(4) (effective June 9, 2018). Next, the Board voted to affirm
the Department’s order. The Board subsequently released written findings of
fact and conclusions of law supporting its decision to affirm the Department’s
issuance of the NRPA and Site Law permits.9
[¶14] In its written findings, the Board addressed several issues,
including the impacts of Kingfish’s project on water quality and neighboring
wildlife. With regard to the impacts on water quality, the Board concluded that
Petitioners, by not raising it here or before the Superior Court, have waived any challenge to the
8
Board’s exercise of discretion in declining to conduct another hearing to receive additional public
input and evidence. See Holland v. Sebunya, 2000 ME 160, ¶ 9 n.6, 759 A.2d 205.
9 In the written decision, the Board found that Petitioners had standing to appeal based on
Petitioners’ assertion that the project could cause them to suffer “a potential particularized injury to
lands [or other property interests] held in ownership” by them. No party has challenged Petitioners’
standing.
9
the Department did not err in relying on the previously granted discharge
permit to determine that Kingfish’s project complied with the relevant
standards under NRPA, see 38 M.R.S. § 480-D(5). The Board reasoned as
follows:
When the Department reviews water quality impacts under the
NRPA in a case in which a [discharge permit] application is being or
has separately been evaluated, the focus of the NRPA review is
impacts from regulated activities such as dredging, filling, disturbing
soil, and placement of structures in, on, over, or adjacent to wetlands
and waterbodies. In this context, the direct discharge of
wastewater would be analyzed in the context of the [discharge
permit] application review, and compliance with the NRPA licensing
criteria is based on how the project complies with Chapter 310,
protecting wetlands and waterbodies, and Chapter 335, protecting
significant wildlife and fisheries habitat.
....
Appellants challenge the findings underlying [the discharge
permit] in this appeal of the Site Law and NRPA permit decision,
but the Board finds no error in the Department’s reliance on
another valid Department order, and will not consider a challenge
to the findings made in that license in the context of this appeal. . . .
The Board finds that [Kingfish] complied with the Department’s
regulations by submitting evidence of a valid [discharge permit]
and on that basis finds that the effluent discharge from the
proposed project will not have an unreasonable adverse effect on
water quality.
(Emphasis added and footnote omitted.)
[¶15] With respect to the effects of the project on wildlife and fisheries,
the Board stated:
10
While [Sierra Club and Petitioners] both primarily raise wildlife
and fisheries concerns associated with the waste discharge, and
issues addressed in that licensing process, some issues they raise
are appropriately subject to review under the NRPA or Site Law
licensing criteria.
The Board observed that “the Department solicit[ed] comments from sister
agencies with subject matter expertise, such as the Department of Marine
Resources (DMR) and the Department of Inland Fisheries and Wildlife
(MDIFW).” The Board determined that the input from Marine Resources and
Inland Fisheries and Wildlife constituted evidence that “supports the
Department’s findings on the effects of the discharge on fisheries.”10
Specifically with regard to the construction of the intake and outfall pipes, the
Board found that modifications agreed to by Kingfish in conjunction with the
special conditions ordered by the Department “minimize[] impacts[,] and those
impacts that will occur will be temporary and unlikely to cause a significant
disturbance to relevant species.” The Board concluded:
On the basis of this evidence, and the DMR comments, the Board
finds that the proposed project will not unreasonably harm any
10The Board stated that “each agency availed themselves of the opportunity to comment on the
project and, while MDIFW expressed concerns regarding peatland habitat, and DMR expressed
concerns regarding potential for gear entanglement, neither agency expressed any concerns
regarding any threatened or endangered species.” The Board further credited the Department of
Maine Resources comments that the pipeline construction and ef luent discharge should have little
or no long-term impact on lobster biology or the lobster industry, that the ef luent discharge does not
appear to threaten the scallop population, and that the proposed project should not result in
signi icant adverse impacts to marine resources.
11
significant wildlife habitat, freshwater wetland plant habitat,
threatened or endangered plant habitat, aquatic or adjacent upland
habitat, travel corridor, freshwater, estuarine or marine fisheries
or other aquatic life, and will not cause an undue adverse effect on
the natural environment.
[¶16] Petitioners timely appealed to the Superior Court. See M.R. Civ. P.
80C; 5 M.R.S. § 11002(3) (2024).
B. Rule 80C Review
[¶17] In their appeal to the Superior Court, Petitioners challenged the
agency’s interpretation of its obligations under NRPA and its failure to conduct
an independent assessment under NRPA of the unreasonableness of the harm
that the project would cause to wildlife habitats.11 Petitioners contended that
the NRPA standards for assessing impacts on wildlife are distinct from those
applicable to the discharge licensing process.
[¶18] The court determined that the Board had undertaken an
independent assessment of the impacts on wildlife associated with the
installation of the pipes but not of specific wildlife impacts associated with
wastewater discharge. It nonetheless affirmed the Board’s decision, stating
11In their Rule 80C petition, Petitioners also contended that the agency’s issuance of a NRPA
permit was erroneous because the agency failed to assess whether King ish adequately complied with
its obligation to analyze practicable, less environmentally damaging alternatives to the proposed
project. See 06-096 C.M.R. ch. 310, §§ 5(A), 9(A) (effective Nov. 11, 2018). The Superior Court did
not address this issue, and we do not consider it either because it was presented neither to the Board
nor to us. See Holland, 2000 ME 160, ¶ 9 n.6, 759 A.2d 205.
12
that the Board “did not contravene the letter or purpose of NRPA by forgoing
an independent analysis of the harms associated with the proposed wastewater
discharge and by relying on the findings of the previously issued discharge
permit.” The court determined that although the Board was not prohibited
from considering the impacts on wildlife resulting from the pipes’ use, it was
not obligated to do so because wastewater discharge is not an activity regulated
by NRPA. The court further concluded that the Board’s decision to forgo an
independent inquiry was reasonable because the impacts of the proposed
discharge had been analyzed during the discharge permit approval process,
and the standards for assessing impacts on wildlife at each of the two
permitting stages were not so divergent as to constitute an error of law.
[¶19] Petitioners timely appealed to us. See M.R. App. P. 2B(c)(1);
14 M.R.S. § 1851 (2024).
II. DISCUSSION
[¶20] As they did in the Superior Court, Petitioners advance two
principal arguments here. First, they contend that the Board was required
under NRPA to assess the impact on wildlife habitat by the use of the intake and
outfall pipes in discharging effluent into Chandler Bay. Second, they argue that
the Board abused its discretion by relying on the Department’s issuance of the
13
discharge permit instead of conducting its own independent analysis to
determine whether or not the intended use of the pipes to discharge treated
wastewater would unreasonably harm wildlife habitat.
A. Standard of Review
[¶21] When the Superior Court acts in its intermediate appellate capacity
under M.R. Civ. P. 80C, we review the agency’s decision directly. Uliano v. Bd. of
Env’t Prot., 2009 ME 89, ¶ 12, 977 A.2d 400. Because the Board acted as the
factfinder and reviewed the legal issues de novo, 06-096 C.M.R. ch. 2, § 24(G)
(effective June 9, 2018), it is the Board’s decision that we review on appeal,
see Passadumkeag Mountain Friends v. Bd. of Env’t Prot., 2014 ME 116, ¶¶ 9-10,
102 A.3d 1181; Concerned Citizens to Save Roxbury v. Bd. of Env’t Prot., 2011 ME
39, ¶ 17, 15 A.3d 1263. We review the Board’s decision for errors of law, factual
findings unsupported by substantial record evidence, or an abuse of discretion.
Forest Ecology Network v. Land Use Regul. Comm’n, 2012 ME 36, ¶ 28, 39 A.3d
74.
[¶22] When interpreting a statutory scheme that is “both administered
by [an] agency and within the agency’s expertise,” we apply “a two-part
inquiry.” NextEra Energy Res., LLC v. Me. Pub. Utils. Comm’n, 2020 ME 34, ¶ 22,
227 A.3d 1117 (quotation marks omitted). We first determine whether the
14
statute’s language is ambiguous. Id. Then if the statute’s language is
unambiguous, we construe the statute in accordance with its plain meaning. Id.
If the statute’s language is ambiguous, “we defer to the interpretation of a
statutory scheme by the agency charged with its implementation as long as the
agency’s construction is reasonable.” Conservation L. Found., Inc. v. Dep’t of
Env’t Prot., 2003 ME 62, ¶ 23, 823 A.2d 551; see also S.D. Warren Co. v. Bd. of
Env’t Prot., 2005 ME 27, ¶ 4, 868 A.2d 210.
B. The Scope of Review under NRPA
[¶23] To curtail or eliminate environmental threats posed by alterations
to “resources of state significance,” 38 M.R.S. § 480-A, NRPA requires a person
to obtain a permit before undertaking a specified “activity” when “the activity
is located in, on or over any protected natural resource or is located adjacent to
. . . [a] coastal wetland,” 38 M.R.S. § 480-C(1)(A). Section 480-C(2) specifies the
“activities” requiring a permit under NRPA:
2. Activities requiring a permit. The following activities require a
permit:
A. Dredging, bulldozing, removing or displacing soil, sand,
vegetation or other materials;
B. Draining or otherwise dewatering;
C. Filling, including adding sand or other material to a sand
dune; or
15
D. Any construction, repair or alteration of any permanent
structure.
Id. § 480-C(2) (emphasis added).
[¶24] If an “activity” requires a permit, NRPA provides that the
Department “shall grant a permit when it finds that the applicant has
demonstrated that the proposed activity meets the standards set forth in
subsections 1 to 11.” 38 M.R.S. § 480-D (emphasis added). Here, the NRPA
standard that Petitioners contend the Board failed to properly consider
requires that “[t]he activity will not unreasonably harm any significant wildlife
habitat, . . . aquatic or adjacent upland habitat, . . . freshwater, estuarine or
marine fisheries or other aquatic life.” 38 M.R.S. § 480-D(3).
[¶25] Kingfish’s proposed installation of intake and outfall pipes
requires a NRPA permit because it will involve regulated “activities” listed in
section 480-C, including “construction” and “dredging” in a coastal wetland.
See 38 M.R.S. § 480-C(2)(A), (D). Petitioners do not challenge the Board’s
evaluation of the impact of these activities. Rather, they assert that NRPA also
requires the Board and the Department to analyze the specific effects of the
effluent discharge into Chandler Bay.
16
[¶26] The statute’s plain language provides otherwise. The list in section
480-C(2) of “activities” triggering Department review in connection with an
application for a permit under NRPA is specific and unambiguous. The statute
reflects a clear intention on the part of the Legislature to subject only certain,
defined “activities” to review under the NRPA standards in section
480-D(1)-(11). See Uliano, 2009 ME 89, ¶ 17, 977 A.2d 400 (holding that the
NRPA standards in section 480-D “only appl[y] to the specific activities listed in
Section 480-C(2)(A)-(D)”); Murphy v. Bd. of Env’t Prot., 615 A.2d 255, 258
(Me. 1992) (noting that NRPA applies to only the particular activities listed in
section 480-C(2)). The discharge of treated wastewater through use of the
operation’s outfall pipes is not a specified activity under section 480-C(2).
[¶27] Petitioners argue that even if the plain language of section 480-C
does not expressly provide that the intended use of the facility (and the intake
and outfall pipes, specifically) is an activity subject to NRPA review, the use
should “factor into the Department’s decision about whether to grant a NRPA
permit to construct an aquaculture facility” because we have “declined to adopt
such a restrictive view of . . . Section 480-C(2).” Petitioners rely on Hannum v.
17
Bd. of Env’t Prot., 2006 ME 51, ¶ 10, 898 A.2d 392, in support of this assertion.12
Their argument is unpersuasive.
[¶28] In Hannum, a trustee of property challenged the Board’s denial of
a permit under NRPA to install a pier and floating dock on the shore of the
property, which was in a coastal wetland. Id. ¶¶ 2-3, 7-8. The trustee argued
that the Board’s decision was in error because it was based not only on whether
the construction of the dock itself would harm wildlife but also on the Board’s
determination that the use of the dock would “increase boat traffic in the cove
which [would] disturb the existing tern and seal colonies.” Id. ¶¶ 12-15
(quotation marks omitted). We affirmed the Board’s decision, concluding that
“the Board has the power to deny a permit application for a dock based on the
dock’s use.” Id. ¶ 14.
[¶29] To be clear, in Hannum we did not say that the agency is obligated
under NRPA to consider the expected effects on wildlife of the intended use of
a structure or facility. Rather, Hannum held that it was within the agency’s
12 Petitioners also argue that an interpretation of section 480-C(2) that con ines the scope of NRPA
review to the speci ic activities listed is inconsistent with past Department practice of “routinely
consider[ing] long-term use when determining whether to issue permits under NRPA.” Because this
argument was not raised before either the Board or the Superior Court, we decline to consider it.
Cf. Off. of the Pub. Advoc. v. Pub. Utils. Comm’n, 2023 ME 77, ¶¶ 27-28, 306 A.3d 633 (concluding that
an argument alleging the Public Utilities Commission’s failure to create an evidentiary record was
waived since it was not raised to the Commission); Indus. Energy Consumer Grp. v. Pub. Utils. Comm’n,
2024 ME 60, ¶¶ 28-31, 320 A.3d 437 (declining to review a federal preemption challenge in the
absence of a “fully developed administrative record”).
18
discretion to take those impacts into consideration in evaluating compliance
with the standard in 38 M.R.S. § 480-D(3). See id. ¶¶ 11, 14 (“[W]e will accord
deference to the Board’s reasonable conclusion that it may examine the impact
of the use of a structure for which a permit is required along with the impact of
the structure itself.” (emphasis added)).
[¶30] The Board, therefore, did not err in focusing its NRPA evaluation
in this case on the “activities” listed in section 480-C(2) relating to the
installation of the intake and outfall pipes. It was not required in this instance
to assess the impact of the use, as opposed to the installation, of the facility’s
intake and outfall pipes because, as the Board stated, the impacts of the direct
discharge of wastewater “[had] separately been evaluated” by the Department
in the context of Kingfish’s application for the discharge permit. Whether the
Board’s reliance on that prior approval was reasonable and a proper exercise
of its discretion is the subject of Petitioners’ second principal argument, which
we address next.
C. The Board’s Reliance on the Discharge Permit
[¶31] Petitioners contend that the Board’s decision to rely on the
Department’s previously issued discharge permit to satisfy NRPA requirements
rather than to conduct its own independent analysis was an abuse of discretion.
19
They argue that the standards for assessing environmental harm in connection
with the discharge permit are significantly different from the applicable NRPA
standard, and further that the allowance of “economic or social benefits,”
38 M.R.S. § 414-A(1)(C), to counterbalance potential water quality degradation
in evaluating a discharge permit application renders reliance on those
standards unreasonable in the context of reviewing an application for a NRPA
permit.
[¶32] We conclude that the Board did not abuse its discretion in relying
on the previously issued discharge permit and that the reliance was reasonable
when the Board was determining whether Kingfish’s proposed project would
not “unreasonably harm any significant wildlife habitat” or “other aquatic life.”
38 M.R.S. § 480-D(3). The discharge licensing process considers impacts on
wildlife in two ways. First, the requirements to obtain a permit focus upon
whether a proposed discharge would interfere with a water body’s
classification,13 which is a metric that accounts for impacts on marine habitat
13 The relevant portions of section 414-A require that “[t]he discharge . . . will not lower the
quality” of a “classi ied” or “unclassi ied” body of water below the relevant classi ication. 38 M.R.S.
§ 414-A(1)(A), (B); see also 38 M.R.S. § 413(10)(B) (2024) (imposing this requirement in connection
with marine aquaculture projects). Section 414-A also requires ef luent limitations, see 38 M.R.S.
§ 414-A(1)(D), and prohibits discharges that lower water quality by any amount at all—even if the
water classi ication remains the same—unless “following opportunity for public participation, the
department inds that the discharge is necessary to achieve important economic or social bene its,”
id. § 414-A(1)(C).
20
and wildlife. For instance, Chandler Bay’s status as a Class SB water body
requires that it be “suitable . . . as habitat for fish and other estuarine and marine
life”; that it not receive “[d]ischarges” that “cause adverse impact to estuarine
and marine life”; and that it comply with numeric limitations, including
standards for dissolved oxygen concentration.14 See 38 M.R.S.
§ 465-B(2)(A)-(C). Second, the Department must, in deciding whether to issue
a discharge permit, find that “the proposed activity would not have a significant
impact on” an “existing in-stream use . . . of the water body by a population of
plant life, wildlife, or aquatic, estuarine or marine life” or on their respective
habitats. See 38 M.R.S. § 464(4)(F)(1-A)(a).
[¶33] In granting the discharge permit to Kingfish, the Department
examined the effects of the intended discharge from the outfall pipes on wildlife
habitat and aquatic life and made findings consistent with these statutory
14 We note that 38 M.R.S. § 465-B(2)(B) was amended to add an introductory sentence that reads,
“Class SB waters must be of suf icient quality to support all estuarine and marine species indigenous
to those waters without detrimental changes in the resident biological community.” P.L. 2021, ch. 551,
§ 15 (effective Aug. 8, 2022) (codi ied at 38 M.R.S. § 465-B(2)(B) (2024)). As considered in this case,
the amendment is of little consequence because (i) it took effect after King ish’s completed discharge
permit application was iled, see supra n.2, and (ii) even if it applied to the circumstances here, the
prefatory standard added to subsection (B) (“waters must be of suf icient quality to support all
estuarine and marine species indigenous to those waters without detrimental changes in the resident
biological community”) would essentially overlap with the standard in subsection (C) (“[d]ischarges
to Class SB waters may not cause adverse impact to estuarine and marine life in that the receiving
waters must be of suf icient quality to support all estuarine and marine species indigenous to the
receiving water without detrimental changes in the resident biological community”), 38 M.R.S.
§ 465-B(2)(C) (emphasis added).
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requirements. It found that the proposed discharge would not lower the
classification status of any water body and that “[e]xisting in-stream water use
will be maintained and protected.” And, as noted above, the discharge permit
includes ongoing sampling and monitoring requirements intended to protect
aquatic life and habitat as well as authority for the Department to modify or
require different effluent limits “where there is a reasonable potential that the
effluent may cause water quality criteria to be exceeded.” See supra ¶ 6.
[¶34] Finally, contrary to Petitioners’ argument, the Board’s reliance on
the discharge permit in the context of the NRPA review in this instance was not
unreasonable because the Department considered the project’s economic and
social benefits under the State’s antidegradation policy. Even when considering
economic and social benefits, the Department still cannot issue the permit if it
determines that the discharge will “cause or contribute to the failure of the
water body to meet the standards of classification.” 38 M.R.S. § 464(4)(F)(3).
Nor may the Department issue a permit where the discharge “would cause
unreasonable degradation of marine waters.” 38 M.R.S. § 464(4)(A)(11). And
particularly for Chandler Bay, a Class SB water body, any discharge “may not
cause adverse impact to estuarine and marine life.” 38 M.R.S. § 465-B(2)(C).
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[¶35] Accordingly, the Board did not err in interpreting the scope of
review under NRPA or abuse its discretion in relying upon the Department’s
separate evaluation of impacts of the intended effluent discharge.
The entry is:
Judgment affirmed.
Elizabeth A. Boepple, Esq. (orally), Sean R. Turley, Esq., and Ellen P. Masalsky,
Esq., Murray, Plumb & Murray, Portland, for appellant Eastern Maine
Conservation Initiative and Roque Island Gardner Homestead Corporation
Aaron M. Frey, Attorney General, Robert L. Martin, Asst. Atty. Gen. (orally), and
Jack Dafoe, Asst. Atty. Gen., Of ice of the Attorney General, Augusta, for appellee
Board of Environmental Protection
Patrick I. Marass, Esq. (orally), Katherine A. Joyce, Esq., and Rachael McEntee,
Esq., Bernstein Shur, Portland, for appellee King ish Maine, Inc.
Kennebec County Superior Court docket number AP-2022-33
FOR CLERK REFERENCE ONLY