Amicus Curiae Brief — Weyerhaeuser Company, Petitioner v. United States Fish and Wildlife Service, et al.
Supreme Court briefApr 30, 2018
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No. 17-71
IN THE
Supreme Court of the United States
————
WEYERHAEUSER COMPANY,
Petitioner,
v.
UNITED STATES FISH AND WILDLIFE SERVICE, et al.,
Respondents.
————
On Writ of Certiorari to the
United State Court of Appeals
for the Fifth Circuit
————
BRIEF OF AMICUS CURIAE
ENERGY AND WILDLIFE ACTION COALITION
IN SUPPORT OF PETITIONER
————
STEVEN P. QUARLES
NOSSAMAN LLP
1666 K Street, NW
Suite 500
Washington, D.C. 20006
(202) 887-1400
BROOKE M. WAHLBERG
NOSSAMAN LLP
816 Congress Avenue
Suite 970
Austin, TX 78701
(512) 651-0660
SVEND A. BRANDT-ERICHSEN
Counsel of Record
NOSSAMAN LLP
601 Union Street
Suite 5305
Seattle, WA 98102
(206) 395-7632
sbrandterichsen@nossaman.com
Counsel for Amicus Curiae Energy and
Wildlife Action Coalition
April 30, 2018
WILSON-EPES PRINTING CO., INC. – (202) 789-0096 – WASHINGTON, D. C. 20002
TABLE OF CONTENTS
Page
TABLE OF AUTHORITIES ................................
iii
INTEREST OF THE AMICUS CURIAE ............
1
SUMMARY OF ARGUMENT .............................
3
ARGUMENT ........................................................
6
I. The ESA dictates that “critical habitat”
must be habitable .....................................
6
A. The operative provisions of the ESA
plainly state that critical habitat
must be habitable ................................
6
B. The Fifth Circuit’s analysis ignored
the operative provisions of the ESA
and the plain meaning of the word
“habitat.” ..............................................
9
C. The Service’s determination that
lands may be deemed “essential to the
conservation of a species” even though
not habitable by that species now or
in the reasonably foreseeable future is
not entitled to Chevron deference .......
13
II. Designating areas that are not habitable
by a listed species as “critical habitat”
harms the development and operation of
the nation’s energy infrastructure ...........
16
A. The electric energy industry in the
United States is investing heavily in
new generation, transmission and
distribution facilities and in enhancing the nation-wide electric grid .........
17
(i)
ii
TABLE OF CONTENTS—Continued
Page
B. Energy projects that could have an
adverse effect on critical habitat face
significant costs, likely delays, and
higher operating costs .........................
20
C. Energy project developers seek to
avoid or minimize the impact of new
electricity generation, transmission,
and distribution infrastructure within
critical habitat .....................................
27
D. Extending ESA “critical habitat” protection to lands that cannot sustain a
listed species threatens to disrupt the
development and operation of the
nation’s energy infrastructure ............
29
CONCLUSION ....................................................
33
iii
TABLE OF AUTHORITIES
CASES
Page(s)
Chevron, U.S.A., Inc. v. Nat. Res.
Def. Council, Inc.,
467 U.S. 837, 104 S. Ct. 2778 (1984) .......passim
City of Arlington, Tex. v. Fed.
Commc’ns Comm’n,
569 U.S. 290, 133 S. Ct. 1863 (2013) ........ 15-16
Dolan v. U.S. Postal Serv.,
546 U.S. 481, 126 S. Ct. 1252 (2006) ........ 7, 10
Food and Drug Admin. v. Brown
& Williamson Tobacco Corp.,
529 U.S. 120, 120 S. Ct. 1291 (2000) ........ 14, 15
Mich. v. Envtl. Prot. Agency,
576 U.S. __, 135 S. Ct. 2699 (2015) ..........
16
Nat’l Ass’n of Home Builders v.
Defenders of Wildlife,
551 U.S. 644, 127 S. Ct. 2518 (2007) ........ 13, 14
Perrin v. U.S.,
444 U.S. 37, 100 S. Ct. 311 (1979) ............
8
United Sav. Assn. of Tex. v. Timbers
of Inwood Forest Assocs., Ltd.,
484 U.S. 365, 108 S. Ct. 626 (1988) ..........
14
Util. Air Regulatory Grp. v.
Envtl. Prot. Agency,
573 U.S. ___, 134 S. Ct. 2427 (2014) ........ 14, 15
STATUTES AND REGULATIONS
16 U.S.C. § 1531(b) .......................................
6, 8
16 U.S.C. § 1532(5)(A) ..................................
3
iv
TABLE OF AUTHORITIES—Continued
Page(s)
16 U.S.C. § 1532(5)(A)(i) ............................ 7, 9, 12
16 U.S.C. § 1532(5)(A)(ii) ............................passim
16 U.S.C. § 1532(5)(C) .................................passim
16 U.S.C. § 1533(a) ......................................passim
16 U.S.C. § 1533(a)(3)(A)..............................
3, 4
16 U.S.C. § 1533(a)(3)(A)(i) .........................passim
16 U.S.C. § 1533(a)(3)(A)(ii) .........................
6
16 U.S.C. § 1536 ..........................................passim
16 U.S.C. § 1536(a)(2)..................................passim
33 U.S.C. § 1344 ..........................................passim
33 C.F.R. § 330.1(b) ......................................... 21, 22
33 C.F.R. § 330.4(f)(2) ....................................
22
43 U.S.C. § 1761 ...........................................
24
50 C.F.R. § 402.02(c).....................................
24
50 C.F.R. § 402.12 ..........................................
20
50 C.F.R. § 402.14(a) ....................................
20
50 C.F.R. § 402.14(c) ......................................
20
50 C.F.R. § 402.14(g) ....................................
21
50 C.F.R. § 402.14(h) .................................... 21, 25
50 C.F.R. § 402.16(d) ......................... 20, 25, 30-31
Issuance and Reissuance of Nationwide
Permits, 82 Fed. Reg. 1860 (Jan. 6, 2017) ...
22
v
TABLE OF AUTHORITIES—Continued
OTHER AUTHORITIES
Page(s)
American Wind Energy Association, U.S.
Wind Industry Fourth Quarter 2017
Market Report (January 25, 2017),
available at: http: //awea.files.cms-plus.
com/FileDownloads/pdfs/4Q%202017%2
0AWEA%20Market%20Report%20Publi
c%20Version.pdf........................................
18
Edison Electric Institute, Historical and
Projected Transmission Investment
(September 2017), available at: http://
www.eei.org/issuesandpolicy/transmissio
n/Documents/bar_Transmission_Investm
ent.pdf ......................................................
18
Edison Electric Institute, Transmission,
available at: http://www.eei.org/issues an
dpolicy/transmission/Pages/default.aspx
(last visited April 25, 2018) .....................
5
Federal Energy Regulatory Commission,
Office of Enforcement, Energy Market
Snapshot (June 2017), available at:
https://www.ferc.gov/market-oversight/mk
t-snp-sht/2017/06-2017-snapshot-nationa
l.pdf ............................................................
5
“Habitat,” Merriam-Webster Dictionary
(11th ed. 2016) ..........................................
8
John Ruhs, Acting Deputy Director for
Operation, BLM, Statement before the
Senate Committee on Energy and Natural
Resources (September 19, 2017), available at: https://www.doi.gov/ocl/electricinfrastructure-vegetation-management ..
24
vi
TABLE OF AUTHORITIES—Continued
Page(s)
NERC FAC-003-4, Transmission Vegetation Management (October 1, 2016),
available at: https://www.nerc.com/pa/
Stand/Reliability%20Standards/FAC-0034.pdf ........................................................... 25, 26
Solar Energy Industry Association, U.S.
Solar Market Through 2017: Key
Takeaways, available at: https://www.
seia.org/solar-industry-research-data (last
visited April 25, 2018) ..............................
18
U.S. Fish and Wildlife Service and National
Marine Fisheries Service, Endangered
Species Consultation Handbook, Procedures for Conducting Consultation and
Conference Activities Under Section 7 of
the Endangered Species Act (March
1998), available at: https://www.fws.gov/
endangered/esa-library/pdf/esa_section7_
handbook.pdf ............................................. 23, 30
U.S. Fish & Wildlife Service, Land-Based
Wind Energy Guidelines (March 23,
2012), available at: https://www.fws.gov/
ecological-services/es-library/pdfs/WEG_
final.pdf .....................................................
28
INTEREST OF THE AMICUS CURIAE1
The Energy and Wildlife Action Coalition (“EWAC”)
respectfully submits this brief as amicus curiae in
support of Petitioner Weyerhaeuser Company. EWAC
is an unincorporated association headquartered in
Washington, D.C. comprised of electric utilities, electric transmission and distribution providers, renewable
energy companies, and related trade associations. EWAC
members operate throughout the United States.
EWAC’s fundamental goal is to evaluate, develop,
and promote reasonable environmental policies for
federally protected wildlife and closely related natural
resources while ensuring the continued generation
and transmission of reliable and affordable electricity.
EWAC supports public policies, based on sound science,
that protect wildlife and natural resources in a reasonable, consistent, and cost-effective manner.
The Fifth Circuit’s ruling, if affirmed by this Court,
would have a significant negative impact on EWAC
members. EWAC’s members develop, construct, maintain, own, and operate electric generation, transmission,
and distribution facilities that are located or proposed
to be built on private and public lands, including lands
that are not habitable by threatened or endangered
species (“listed species”), and yet these areas could be
designated as critical habitat for listed species under
1
Pursuant to Sup. Ct. R. 37.6, amicus curiae states that no
counsel for a party has written this brief in whole or in part, and
that no person or entity, other than amicus curiae, its members,
or its counsel, has made a monetary contribution to the preparation or submission of this brief. Pursuant to Sup. Ct. R. 37.3(a),
Petitioner and Respondents have provided blanket written consent to the filing of amicus briefs in this matter and their written
consent is on file.
2
the criteria upheld by the divided panel of the Fifth
Circuit.
Federal agencies are required to consult with the
U.S. Fish and Wildlife Service (“Service”) under
section 7(a)(2) of the Endangered Species Act (“ESA”),
16 U.S.C. § 1536(a)(2), if a proposed facility is located
on or crosses federal lands, requires a federal permit
or approval, or receives federal financial support and
may adversely affect a listed species or critical habitat.
In other words, if critical habitat is present in any of
these scenarios, section 7(a)(2) triggers additional
review.
Thus, for example, many EWAC members have
existing facilities on federal lands and will continue to
construct new facilities across federal lands, often
with few if any practical alternative locations, to meet
the electricity needs of their customers. The siting of
such infrastructure requires federal authorization and
so can trigger section 7 review, including as to impacts
on critical habitat. Furthermore, once constructed,
electric energy infrastructure is likely to remain on the
land for many decades. Critical habitat designations
can affect the renewal of authorization for use of the
federal lands, affecting existing infrastructure and
constraining operation and maintenance of existing
facilities on both private and public lands.
Further, many EWAC members’ facilities on public
or private lands require federal approvals such as
Clean Water Act (“CWA”) section 404 permits and
Federal Energy Regulatory Commission (“FERC”)
licenses and some receive federally backed financing.
Again, these federal actions can trigger section 7. And
even absent the need for federal approvals, the existence of critical habitat or the threat of a potential
critical habitat designation within a facility’s footprint
3
complicates private financing, as lenders and investors react to the increased costs and risks posed by
critical habitat, which can increase the cost of capital
or result in financial reserve requirements, bonding or
parent company guarantees, all of which make financing more difficult and more expensive and can even
result in the demise of the project.
SUMMARY OF ARGUMENT
The Fifth Circuit wrongly upheld a decision by the
Service that unlawfully designated an area in Louisiana
as “critical habitat” for the endangered dusky gopher
frog (Rana sevosa) even though there is no occurrence
of the species on those lands, that area cannot sustain
the species, now or in the foreseeable future, and there
is no connection to any area that is actually habitable
by that species. See Pet. App. 1a-77a.
In reviewing the Service’s action, the Fifth Circuit
incorrectly limited its analysis to the ESA’s definitions
of occupied and unoccupied “critical habitat,” 16 U.S.C.
§ 1532(5)(A), and ignored the criteria for critical habitat contained in sections 4 and 7 of the ESA, the
statute’s operative provisions, which specify that critical habitat is a subset of the habitat of a listed species.
16 U.S.C. §§ 1533(a)(3)(A), 1536(a)(2); Pet. App. 15a,
18a, 23a-32a.
The Fifth Circuit’s narrow focus on the ESA’s
definition of “critical habitat,” to the exclusion of the
operative provisions of the statute, allowed it to
wrongly conclude: “There is no habitability requirement in the text of the ESA or the implementing
regulations.” Pet. App. 23a.
To the contrary, the requirement that critical
habitat be part of the habitat of a species is a plain and
unambiguous requirement of the ESA. When the
4
Service lists a species under the ESA, the statute
directs the Service, “to the maximum extent prudent
and determinable,” to designate by regulation “any
habitat of such species which is then considered to be
critical habitat.” 16 U.S.C. § 1533(a)(3)(A) (emphasis
added). The ESA also requires federal agencies to
consult with the Service before undertaking or
authorizing an action that is likely to destroy or
adversely modify “habitat . . . which is determined . . .
to be critical.” 16 U.S.C. § 1536(a)(2).
The Fifth Circuit also improperly deferred to the
Service’s interpretation of the phrase “essential to the
conservation of the species” in the ESA’s definition of
unoccupied critical habitat, 16 U.S.C. § 1532(5)(A)(ii),
wrongly concluding that this phrase is the sole test for
designating unoccupied critical habitat and accepting
a Service interpretation of “essential” that conflicts
with the plain and unambiguous requirement of
section 4 of the ESA that critical habitat be “habitat of
such species.” 16 U.S.C. § 1533(a)(3)(A)(i).
As a result of these errors, the Fifth Circuit blessed
a standard that allows an area to be designated as
“critical habitat” even if it is currently uninhabitable
by a listed species and has no prospect of ever becoming habitable by that species. This fails to recognize
that “critical habitat” is, first and foremost, habitat
for a listed species. Among other consequences, this
unlawfully broad reading of critical habitat would
impose an unworkable and unreasonable regulatory
burden on the development and continuing operation
of electric energy infrastructure throughout the country.
Electricity generation, transmission and distribution facilities are located throughout the United
States. The total available installed electrical generating capacity in the United States is currently about
5
1,200 gigawatts from all sources (conventional and
renewable).2 The electric transmission network is the
backbone of the nation’s energy grid and consists of
more than 600,000 circuit miles of lines, 240,000 of
which are considered high-voltage lines.3 There is also
a spider web of distribution lines delivering electricity
from substations to consumers. Electricity generation,
transmission and distribution facilities may be found
in every corner of our country. As a result, the electric
energy industry frequently interacts with listed species
and critical habitat and has a profound interest in the
proper designation of critical habitat for listed species.
There are real consequences for the nation’s
electricity generation, transmission, and distribution
infrastructure that will result from designating areas
uninhabitable by a listed species as “critical habitat”
and from extending the protections of the ESA to those
areas. Through this amicus brief, EWAC offers the
Court a window into how the Fifth Circuit’s decision
could disrupt the development and ongoing operation
of its members’ facilities.
2
Federal Energy Regulatory Commission, Office of Enforcement, Energy Market Snapshot (June 2017), available at:
https://www.ferc.gov/market-oversight/mkt-snp-sht/2017/06-2017snapshot-national.pdf.
3
Edison Electric Institute, Transmission, available at: http://
www.eei.org/issuesandpolicy/transmission/Pages/default.aspx.
6
ARGUMENT
I. The ESA dictates that “critical habitat”
must be habitable.
A. The operative provisions of the ESA
plainly state that critical habitat must
be habitable.
One of the purposes of the ESA is “to provide a
means whereby the ecosystems upon which endangered species and threatened species depend may be
conserved.” 16 U.S.C. § 1531(b). The ESA is structured to protect the ecosystems upon which a listed
species depends through its provisions for designating
and protecting habitat that is determined to be critical
for that species – section 4 (the designation of critical
habitat) and section 7 (federal interagency consultation). 16 U.S.C. §§ 1533(a), 1536.
By its terms, section 4 of the ESA does not authorize
the Service to designate an area that is not habitable
by a listed species as “critical” for that species. It
directs that, when the Service lists a species, it shall,
“to the maximum extent prudent and determinable,”
designate by regulation “any habitat of such species
which is then considered to be critical habitat.” 16
U.S.C. § 1533(a)(3)(A)(i) (emphasis added). Under this
provision, lands that are not “habitat of such species”
cannot be “critical habitat.”
Section 4’s criteria for “critical habitat” also include
a temporal element: designation is limited to habitat
that is considered critical at the time the species is
listed (“then considered to be”). Id. The designation
of critical habitat may be revised “from time-to-time
thereafter as appropriate,” id. at § 1533(a)(3)(A)(ii),
which allows the Service to account for changes in
habitat over time. But nothing in section 4 authorizes
7
the Service to designate as “critical” an area that is not
currently habitable by the species, even if it might
become habitat at some future date.
Using nearly identical phrasing, section 7 of the
ESA also describes critical habitat as a subset of a
species’ existing habitat:
Each Federal agency shall, in consultation
with and with the assistance of the Secretary,
insure that any action authorized, funded, or
carried out by such agency (hereinafter in this
section referred to as an “agency action”) is
not likely to jeopardize the continued existence of any endangered species or threatened
species or result in the destruction or adverse
modification of habitat of such species which
is determined by the Secretary, after consultation as appropriate with affected States, to be
critical [pursuant to section 4] . . . .
16 U.S.C. § 1536(a)(2) (emphasis added). Section 7,
like section 4, is thus explicit that critical habitat must
first and foremost be habitat of the listed species.
The ESA’s definitions (section 3 of the Act) supplement the criteria for designating “critical habitat”
found in section 4, describing different requirements
depending on whether the area was occupied or
unoccupied by the species at the time the species was
listed. 16 U.S.C. §§ 1532(5)(A)(i) and (A)(ii). The
additional criteria contained in these definitions must
be read in conjunction with the unambiguous statements in sections 4 and 7 that critical habitat is a
subset of the habitat for a listed species. See Dolan v.
U.S. Postal Serv., 546 U.S. 481, 486, 126 S. Ct. 1252,
1257 (2006) (“Interpretation of a word or phrase
8
depends upon reading the whole statutory text [and]
considering the purpose and context of the statute.”).
Although the ESA does not expressly define what
constitutes “habitat” for a listed species, the term
“critical habitat” is founded on the concept that the
area being designated must in fact be habitat – that
it is habitable by a listed species. Thus, for example,
the ESA states that, absent special circumstances,
“critical habitat shall not include the entire geographic
area which can be occupied by the threatened or
endangered species.” 16 U.S.C. § 1532(5)(C). The
clear implication is that to be critical habitat for a
listed species, an area must be one that “can be
occupied” by that species. This directive echoes, and
appears intended to be equivalent to, the directive in
ESA sections 4 and 7 that critical habitat be a subset
of habitat for the listed species.
In the absence of an express statutory definition
of “habitat,” the Court must look to the ordinary
meaning of the word and to the way it is used in the
ESA as a whole. “A fundamental canon of statutory
construction is that, unless otherwise defined, words
will be interpreted as taking their ordinary, contemporary, common meaning.” Perrin v. U.S., 444 U.S. 37,
42, 100 S. Ct. 311, 314 (1979).
The Merriam-Webster Dictionary defines “habitat”
as “the place or environment where a plant or animal
naturally or normally lives and grows,” or, as a secondary definition, “the place where something is commonly
found.” “Habitat,” Merriam-Webster Dictionary (11th
ed. 2016). These dictionary definitions are consistent
with the purposes of the ESA, see 16 U.S.C. § 1531(b),
as Congress selected the word “habitat” to refer to the
ecosystems upon which listed species depend. The
dictionary definitions of “habitat” also are consistent
9
with the concept of an area that “can be occupied” by
the species. See 16 U.S.C. § 1532(5)(C). The word
“habitat,” as it is used in the ESA, thus indicates that
the area in question must be capable of sustaining a
particular species even if that species does not
currently occupy the area.
Accordingly, when ESA sections 4 and 7 refer to the
designation of “habitat of such species” as “critical
habitat,” they mean a place where a plant or animal
naturally lives and grows; a place that is capable of
sustaining the species; a place that is habitable by the
species.
B. The Fifth Circuit’s analysis ignored the
operative provisions of the ESA and the
plain meaning of the word “habitat.”
The Fifth Circuit panel, as it upheld the designation
of lands in Louisiana as unoccupied critical habitat for
the dusky gopher frog, limited its analysis to the ESA’s
definitions of occupied and unoccupied critical habitat.
See Pet. App. 15a, 18a, 23a-32a (majority opinion
analyzes only sections 1532(5)(A)(i)-(ii)). It did so
even though those lands cannot sustain the frog today
and are not likely to be capable of doing so in the
reasonably foreseeable future without significant
human manipulation. Id.
The ESA’s definitions differentiate between occupied
and unoccupied critical habitat. Occupied critical
habitat, not surprisingly, must be occupied by the
species at the time the species is listed as threatened
or endangered. 16 U.S.C. § 1532(5)(A)(i). It also must
contain physical and biological features that: (1) are
“essential for the conservation of the species”; and
(2) “may require special management considerations
or protection.” Id. Unoccupied critical habitat is lim-
10
ited to areas that are not occupied at the time of species
listing but nevertheless are deemed “essential for
conservation of the species.” 16 U.S.C. § 1532(5)(A)(ii).
Looking only at these provisions, the Fifth Circuit
determined – wrongly – that the sole criterion the ESA
provides for designating unoccupied critical habitat is
found in section 3(5)(A)(ii), 16 U.S.C. § 1532(5)(A)(ii),
and entails a Service determination that the area is
“essential” for conservation of the listed species. Pet.
App. 15a, 18a, 21a-24a. The Fifth Circuit then ruled
that the ESA does not define “essential,” that the word
is ambiguous, and accordingly that the Service’s
determination that an unoccupied area is “essential”
and so should be designated as critical habitat
(without regard to whether the area is habitable) is
entitled to Chevron deference. Pet. App. 15a, 21a-24a,
citing Chevron, U.S.A., Inc. v. Nat. Res. Def. Council,
Inc., 467 U.S. 837, 843 n.9, 104 S. Ct. 2778 (1984).
The Fifth Circuit found ambiguity by erroneously
focusing exclusively on the word “essential” in section
3(5)(A)(ii) and ignoring the additional criteria for
critical habitat contained in sections 3(5)(C) and 4, 16
U.S.C. §§ 1532(5)(C) and 1533(a)(3)(A)(i). It also
ignored the way the word “habitat” and the phrase
“critical habitat” are used in context in ESA sections 4
and 7, 16 U.S.C. §§ 1533(a)(3)(A)(i) and 1536(a)(2), the
operative provisions of the statute.
Statutory “[i]nterpretation of a word or phrase
depends upon reading the whole statutory text [and]
considering the purpose and context of the statute.”
Dolan, 546 U.S. at 486. “A word in a statute may or
may not extend to the outer limits of its definitional
possibilities.” Id. “[I]f the statute is silent or ambiguous with respect to the specific issue, the question for
the court is whether the agency’s answer is based on a
11
permissible construction of the statute.” Chevron, 467
U.S. at 843. The ESA must be read and considered as
a whole to determine the meaning of “critical habitat.”
By their language and structure, ESA sections 4
and 7 make clear that “critical habitat” – including
unoccupied critical habitat – is a subset of a species’
habitat in existence at the time of the species’ listing,
and as such it must be capable of supporting that
species. The ESA’s definition of unoccupied “critical
habitat” in section 3(5)(A)(ii) informs the application
of sections 4 and 7, but also must be read in harmony
with the use of the term “critical habitat” in those
operative sections of the statute. If any ambiguity
exists in the section 3(5)(A)(ii) definition, then the first
source for guidance must be the rest of the statute –
here, primarily the operative provisions of section 4
and section 7 that authorize the designation of
“habitat of such species” as critical habitat and ensure
that the actions of federal agencies are not likely to
result in the “destruction or adverse modification of
habitat of such species which is determined . . . to be
critical.” See 16 U.S.C. §§ 1533(a)(3)(A)(i), 1536(a)(2).
Further, the Fifth Circuit ignored section 3(5)(C),
another element of the ESA’s definition of “critical
habitat” providing that “critical habitat shall not
include the entire geographic area which can be
occupied by the threatened or endangered species,”
except in circumstances determined by the Service.
16 U.S.C. § 1532(5)(C). This provision reinforces the
directive in section 4 and the implication of section 7
that “critical habitat” should be a subset of the listed
species’ habitat – the “geographic area which can be
occupied” by the species. No reasonable reading of
section 3(5)(C) would authorize the designation of
12
critical habitat that is outside of the geographic area
which can be occupied by a listed species.
The Fifth Circuit dismissed the possibility that
unoccupied critical habitat must be habitable by the
listed species by pointing to differences in the language the ESA uses to define occupied and unoccupied
critical habitat, 16 U.S.C. §§ 1532(5)(A)(i) and (A)(ii).
Pet. App. 23a-24a. Occupied critical habitat must
have “physical and biological features” essential to the
conservation of the species, while unoccupied habitat
must be in “areas” essential for the conservation of the
species. Id. The Fifth Circuit ruled that requiring
unoccupied areas to contain the essential physical and
biological features needed to sustain a listed species
“effectively conflates the standard for designating
unoccupied land with the standard for designating
occupied land.” Id. (emphasis in original).
In so holding, the Fifth Circuit placed too much
weight on the reference to biological and physical
characteristics in section 1532(5)(A)(i), as if this were
the only reference to the suitability of an area to the
listed species to be found in the ESA. To the contrary,
ESA sections 3(5)(C), 4 and 7 plainly state that critical
habitat is a subset of the habitat of a listed species
or a subset of the area that can be occupied by the
species. Occupied critical habitat is distinguished
from unoccupied critical habitat by the fact that it was
occupied by the species at the time the species was
listed. In defining occupied habitat as critical, the
ESA points to the presence of physical and biological
characteristics that are deemed essential to the
conservation of the species, distinguishing “critical
habitat” from “all habitat.” But the ESA, at its base,
requires that both occupied and unoccupied critical
13
habitat be part of the habitat for a listed species. See
16 U.S.C. §§ 1533(a)(3)(A)(i), 1536(a)(2).
The failure to read the term “critical habitat” with
an eye to the context in which that term is used in
sections 4 and 7 and without referencing the additional criteria for critical habitat found in sections
3(5)(C) and 4 resulted in the Fifth Circuit giving
improper Chevron deference to a Service interpretation of the ESA’s definition of unoccupied critical
habitat. “It is a fundamental canon of statutory construction that the words of a statute must be read
in their context and with a view to their place in the
overall statutory scheme.” Nat’l Ass’n of Home
Builders v. Defenders of Wildlife, 551 U.S. 644, 666,
127 S. Ct. 2518, 2534 (2007) (internal quotation
omitted). Failure to follow this basic canon resulted in
Fifth Circuit deference to and adoption of a mistaken
Service interpretation that is patently inconsistent
with the plain meaning of the criteria for critical
habitat set out in other ESA provisions.
C. The Service’s determination that lands
may be deemed “essential to the conservation of a species” even though not
habitable by that species now or in the
reasonably foreseeable future is not
entitled to Chevron deference.
Any ambiguity the Fifth Circuit perceived in the
meaning of “critical habitat” derives from isolating
that term and the word “essential” from how “critical
habitat” is used in operative provisions of the statute
and from the plain meaning of the word “habitat.” The
Fifth Circuit should not have moved beyond the first
step of Chevron and should not have extended deference to the Service’s interpretation.
14
Deference to the Service “is appropriate only where
‘Congress has not directly addressed the precise question at issue’ through the statutory text.” Nat’l Ass’n
of Home Builders, 551 U.S. at 665 (2007) (quoting
Chevron, 467 U.S. at 843).
As this Court has established:
In making the threshold determination under
Chevron, “a reviewing court should not confine itself to examining a particular statutory
provision in isolation.” Rather, [t]he meaning—
or ambiguity—of certain words or phrases
may only become evident when placed in
context . . . It is a fundamental canon of
statutory construction that the words of a
statute must be read in their context and with
a view to their place in the overall statutory
scheme.
Id. at 666 (quoting Food and Drug Admin. v. Brown
& Williamson Tobacco Corp., 529 U.S. 120, 132, 120
S. Ct. 1291, 1300 (2000)) (internal citations omitted).
“A statutory ‘provision that may seem ambiguous in
isolation is often clarified by the remainder of the statutory scheme . . . because only one of the permissible
meanings produces a substantive effect that is compatible with the rest of the law.’” Util. Air Regulatory
Grp. v. Envtl. Prot. Agency, 573 U.S. ___, ___, 134 S. Ct.
2427, 2442 (2014), (quoting United Sav. Assn. of Tex.
v. Timbers of Inwood Forest Assocs., Ltd., 484 U.S. 365,
371, 108 S. Ct. 626, 630 (1988)) (ellipsis in original).
Here, congressional intent is clear that critical
habitat is a subset of the habitat of a listed species. 16
U.S.C. §§ 1532(5)(C), 1533(a)(3)(A)(i), 1536(a)(2). The
Fifth Circuit never considered those provisions. If it
had done so, it would not have erroneously claimed
15
that “there is no habitability requirement in the text
of the ESA.” Pet. App. 23a.
Consistent with the holdings of this Court, the Fifth
Circuit should not have confined itself to examining a
particular statutory provision in isolation, as the
definition of unoccupied critical habitat in section
3(5)(A)(ii) that may otherwise appear ambiguous in
isolation is indeed clarified by the remainder of the
statutory scheme, namely sections 3(5)(C), 4 and 7.
See Food and Drug Admin., 529 U.S. at 132; Util. Air
Regulatory Grp., 573 U.S. at __, 134 S. Ct. at 2442.
The only potential meaning of unoccupied critical
habitat, as defined by ESA section 3(5)(A)(ii), that is
also compatible with the rest of the ESA is that critical
habitat – including unoccupied critical habitat – must
be habitable and thus capable of supporting the species
for which it is designated. See Util. Air Regulatory
Grp., 573 U.S. at __, 134 S. Ct. at 2442. In light of the
statute’s unambiguous directive that critical habitat
be habitable, the Fifth Circuit should have stopped
after the first step in its Chevron analysis.
In any event, the Fifth Circuit’s Chevron step 2
analysis is equally flawed, as it erred in endorsing
the Service’s unreasonable exclusion of habitability
from the criteria for critical habitat. The ESA may
not define the term “essential for the conservation of
the species,” but it has placed boundaries on what may
be considered “essential”; Congress has clearly stated
that critical habitat must in fact be habitable. See
16 U.S.C. §§ 1532(5)(C), 1533(a)(3)(A)(i), 1536(a)(2).
“Even under Chevron’s deferential framework, agencies
must operate ‘within the bounds of reasonable interpretation.’” Util. Air Regulatory Grp. 573 U.S. at ___,
134 S. Ct. at 2442 (quoting City of Arlington, Tex. v.
Fed. Commc’ns Comm’n, 569 U.S. 290, 296, 133 S. Ct.
16
1863, 1868 (2013)). Chevron “directs courts to accept
an agency’s reasonable resolution of an ambiguity in a
statute that the agency administers.” Mich. v. Envtl.
Prot. Agency, 576 U.S. __, __, 135 S. Ct. 2699, 2707
(2015). But an agency’s reading of a statute must still
remain within the bounds of reasonable interpretation. Id.
Reading the ESA to allow an uninhabitable area to
be designated as “critical habitat” strays far beyond
the bounds of reasonable interpretation and cannot
survive judicial scrutiny. See id. (EPA wrongly
interpreted the word “appropriate” in the Clean Air
Act provision as allowing it to ignore costs of pollution
controls).
There are limits to the meaning of “essential,” and
so to the Service’s discretion. Here, the Service
designated as “essential” an area that currently provides no conservation benefit to the dusky gopher frog
and will not do so in the future. To deem an area
“essential” to a species that has no connection to the
areas in Mississippi that are currently occupied by the
species and no foreseeable ability to sustain the
species goes beyond the bounds of reason. Even where
Chevron deference does apply, it has limits, and those
limits were exceeded here. See id.
II. Designating areas that are not habitable
by a listed species as “critical habitat”
harms the development and operation of
the nation’s energy infrastructure.
Critical habitat designation can directly constrain
the location of energy generation, transmission, or
distribution projects, impose permitting delays, cause
higher installation and operating costs, and increase
financing costs. This is particularly true if there is no
17
requirement that the lands in question possess
suitable characteristics to sustain listed species, as
there is no way a project proponent could foresee and
plan for the designation. This, in turn, increases the
cost of energy production and transmission, a cost that
is passed on to consumers unless the company that is
developing or operating the affected facilities is constrained by contract or regulation from doing so. The
practical implications of the Fifth Circuit’s ruling are
evident when applied to the development, operation
and maintenance of the nation’s electric energy
infrastructure.
A. The electric energy industry in the
United States is investing heavily in
new generation, transmission and
distribution facilities and in enhancing
the nation-wide electric grid.
The United States is in the midst of an evolution in
its electric energy infrastructure. The means of
generating electricity have been changing, particularly in the last decade, with planned and completed
retirement of a significant number of conventional
(mainly nuclear and coal-fired) power plants, the
development of new renewable (wind, solar and other
sources) and natural gas-fired generation, and noticeable growth in distributed energy resources (rooftop
solar, small-scale wind, and net metering), energy
storage (battery facilities and electric vehicles) and
efficiency. These trends are expected to continue in
the coming years.
The U.S. wind industry installed 7,017 megawatts
(“MW”) of new electric energy generating capacity and
repowered 2,136 MW of existing capacity in 2017,
bringing the total installed capacity for wind energy
generation in the United States to 89,077 MW, or more
18
than 89 gigawatts (“GW”).4 An additional 28,668 MW
of wind generating capacity was under construction or
in advance development at the end of 2017.5
The U.S. Solar industry installed 10,608 MW in
2017 and now has over 53 GW of total installed solar
generating capacity.6 Solar energy has ranked first or
second in new electric generating capacity additions in
each of the last five years.7
Billions of dollars are also being invested in the
nation’s electric transmission system – over $20 billion
in 2016 and more in 2017.8 The factors driving these
investments include enhancing reliability, grid resiliency and modernization, relieving market congestion,
developing smarter energy infrastructure, improving
economic and market efficiency, and expanding the
transmission system to integrate renewables into an
evolving generation mix. The industry also is making
significant investments in a more dynamic and secure
transmission system. Consistent with federal and
state policies, transmission projects are planned through
the use of open and transparent processes that include
analysis and consideration on a comparable basis of
4
American Wind Energy Association, U.S. Wind Industry
Fourth Quarter 2017 Market Report, available at: http://awea.
files.cms-plus.com/FileDownloads/pdfs/4Q%202017%20AWEA%
20Market%20Report%20Public%20Version.pdf.
5
Id.
6
Solar Energy Industry Association, U.S. Solar Market
Through 2017: Key Takeaways, available at: https://www.seia.
org/solar-industry-research-data.
7
8
Id.
Edison Electric Institute, available at: http://www.eei.org/
issuesandpolicy/transmission/Documents/bar_Transmission_Inv
estment.pdf.
19
proposed transmission solutions and alternate, nontransmission solutions. Justification for new-build or
upgrades of existing facilities has to be provided to the
appropriate regulatory and stakeholder groups.
As discussed below, the understanding of “critical
habitat” endorsed by the Fifth Circuit puts these
investments at risk. Energy infrastructure projects –
both new construction and enhancement of existing
facilities – take years to plan and execute. Once
constructed, they typically remain in service for
decades – 30 or 50 years, or more. Thus, a key
consideration in planning and executing these projects
is not only recognizing and designing the project to
avoid and minimize current potential adverse environmental impacts, but also anticipating and planning
for potential changes in regulatory requirements
during project development and the operating life of
the facility.
The Fifth Circuit has endorsed a regulatory wild
card; it is impossible for an energy project developer to
anticipate and plan for the costs and delays that are
likely to result from the designation of an area that
cannot sustain a listed species, now or in the reasonably foreseeable future, as critical habitat for that
species. The resulting uncertainty can cause needed
energy projects to be delayed or cancelled. And should
projects proceed despite being affected by the designation of uninhabitable “critical habitat,” the resulting
increased costs will likely be passed on to the
residential, commercial and industrial consumers of
electricity, with no discernible biological benefit from
“protecting” an area that cannot sustain the species.
20
B. Energy projects that could have an
adverse effect on critical habitat face
significant costs, likely delays, and
higher operating costs.
The regulatory impact of a critical habitat designation arises under ESA section 7(a)(2), which requires
consultation if some discretionary federal action may
affect a listed species or its critical habitat. See 16
U.S.C. § 1536(a)(2). When an energy facility is located
on or crosses federal lands, requires a federal permit,
or receives federal funding, one or more discretionary
federal actions are likely to be required for the facility
to be developed and additional discretionary federal
actions may occur over the operating life of the project.
A federal agency also may retain sufficient discretionary control during the operating life of the facility that
it is obligated to reinitiate ESA consultation if newly
designated critical habitat may be adversely affected
by operation and maintenance of the facility. See 50
C.F.R. § 402.16(d).
It is common for new and existing energy facilities
to prompt one or more of the potential triggers for ESA
section 7 consultation: federal lands; federal permits;
or federal financing. If critical habitat is present in
any of these scenarios, ESA section 7(a)(2) obligates
the federal action agency to conduct additional review.
If this review results in a finding that the activity may
affect critical habitat, then the agency must complete
a formal consultation with the Service before the
federal action can proceed. 50 C.F.R. § 402.14(a). The
consultation process includes preparation of a biological assessment by the project proponent and the
federal action agency, see 50 C.F.R. §§ 402.12, 402.14(c),
and the issuance of an often lengthy and complex
biological opinion by the Service, imposing a myriad
21
of requirements to reduce impacts. See 50 C.F.R.
§§ 402.14(g) & (h). This additional review and the
requirements imposed can result in significant
increases in the time and cost for the affected project
and changes in the project to minimize and mitigate
for habitat impacts.
A few examples amply demonstrate the challenge
the ESA can pose for energy projects. In many parts
of the country, it is virtually impossible to site
electrical infrastructure of any significant length or
size and avoid stream crossings and wetlands impacts.
If construction includes what the U.S. Army Corps of
Engineers (the “Corps”) has classified as dredging or
filling of waters of the United States (“WOTUS”), then
a permit is needed from the Corps under section 404
of the Clean Water Act (“CWA”). 33 U.S.C. § 1344.
Many linear projects require section 404 permits for
potential WOTUS impacts at multiple crossings along
their routes. A utility scale renewable energy project
likewise may include a number of Corps-regulated
drainages within its project area. The issuance of a
section 404 permit triggers the ESA’s consultation
requirement, which obligates the Corps to consider the
potential effect of the activity on critical habitat. See
16 U.S.C. § 1536(a)(2).
The Corps has developed a streamlined Nationwide
Permit (“NWP”) program under CWA section 404 “to
regulate with little, if any, delay or paperwork certain
activities having minimal impacts.” 33 C.F.R. § 330.1(b).
EWAC members regularly rely on the NWP program
for expedited authorization to construct, operate,
and maintain their facilities. For example, NWP 12
authorizes utility line work with limited impacts on
wetlands and waterbodies:
22
Activities required for the construction,
maintenance, repair, and removal of utility
lines and associated facilities in waters of the
United States, provided the activity does not
result in the loss of greater than 1/2-acre of
waters of the United States for each single
and complete project.
Issuance and Reissuance of Nationwide Permits, 82
Fed. Reg. 1860, 1985 (Jan. 6, 2017).
An activity must adhere to a set of general conditions to be authorized under the NWP. In most
cases the NWP program allows activities to be “selfcertified” without any involvement by the Corps.
General Condition 18, however, requires that nonfederal permittees (such as EWAC members) notify
the Corps if any designated “critical habitat might be
affected or is in the vicinity of the activity, or if the
activity is located in designated critical habitat,” so
that the Corps can meet its obligations under ESA
section 7(a)(2). The Corps has expressly stated that
“might affect” is a “low reporting threshold” to trigger
notification. 82 Fed. Reg. at 1954.
If the notification requirement of General Condition
18 is triggered, the activity cannot proceed until the
Corps has completed its ESA section 7(a)(2) obligations. 33 C.F.R. § 330.4(f)(2). Thus, a project proponent
is thrown into a delayed permitting pathway if critical
habitat might be affected or is within the vicinity of
its NWP activity. Id. If the Service does conclude
that adverse effects are likely and requires formal
consultation, the Service’s Biological Opinion likely
will require the implementation of measures that add
further costs and delays, defeating the NWP objective
of regulating “with little, if any, delay or paperwork.”
33 C.F.R. § 330.1(b).
23
Even where the federal nexus arises out of a small
portion of a project (for example, a single stream
crossing), ESA section 7 analysis can sweep in portions
of a project that do not have a federal nexus. While
the Corps focuses its 404 permitting decision on the
area around NWP-regulated dredging or fill, the
Service will look beyond those areas and evaluate
the entire project for effects to critical habitat. See
U.S. Fish and Wildlife Service and National Marine
Fisheries Service, Endangered Species Consultation
Handbook, Procedures for Conducting Consultation
and Conference Activities Under Section 7 of the
Endangered Species Act (“Section 7 Consultation
Handbook”) at 4-18 (March 1998) (“For example
(Figure 4-6), if the proposed action is a wetland fill
(requiring a federal permit) to accommodate access to
a proposed development (the actual area of impact to
the species), then the development is included in the
action area.”) (“Section 7 Consultation Handbook”).9
The Service’s broad analysis effectively means that a
small federal activity (involving less than ½ acre of
dredge or fill) can federalize the entire project for
purposes of the Service’s review under ESA section
7(a)(2).
Another example is renewable energy projects sited
on federal lands and linear facilities that cross those
lands. The federal Bureau of Land Management
(“BLM”), an agency within the Department of the
Interior, manages about 245 million acres in 12
western states. In several western states, federal
lands managed by BLM and other federal agencies
comprise the vast majority of the land area, making it
9
The Service’s ESA Section 7 Consultation Handbook (March
1998) is available at: https://www.fws.gov/endangered/esa-libr
ary/pdf/esa_section7_handbook.pdf.
24
very difficult to design a project that avoids interacting with federal lands. The siting and construction of
new infrastructure, as well as the operation and
maintenance of existing infrastructure, on federal
lands are subject to rights-of-way (“ROW”) obtained
from the relevant federal agencies. See 43 U.S.C.
§ 1761. BLM has issued thousands of miles of ROWs
for electricity transmission and distribution lines
and currently manages almost 16,000 authorizations
for electricity transmission and distribution facilities
on federal lands.10 The development and operation of
renewable energy generation projects (wind and solar)
on federal lands are subject to the same ROW requirements. The last decade in particular saw a number of
commercial wind and solar energy projects being
permitted and constructed on federal lands. EWAC
members will continue to develop and improve electricity generation distribution and transmission facilities
on federal lands in the future in order to ensure
delivery of safe and reliable electric power across
America.
Similar to section 404 permits, ROW grants are
discretionary federal actions, and therefore trigger the
action agency’s obligation to consult with the Service
under the ESA. 16 U.S.C. § 1536(a)(2). The action
agency must evaluate the effects of granting the
ROW on listed species and critical habitat. 50 C.F.R.
§ 402.02(c). If the ROW has the potential to affect
listed species or critical habitat, the approval of the
ROW is typically conditioned on a suite of measures,
to be undertaken by the entities, that are designed to
10
John Ruhs, Acting Deputy Director for Operation, BLM,
Statement before the Senate Committee on Energy and Natural
Resources (September 19, 2017), available at: https://www.doi.
gov/ocl/electric-infrastructure-vegetation-management.
25
minimize and mitigate for these effects. See 50 C.F.R.
§ 402.14(h) (biological opinions). These conservation
measures may force redesign of a project and impose
restrictions on ongoing operations and maintenance.
As previously noted, energy infrastructure projects, once established, are likely to remain on the
landscape for several decades. In many instances,
ESA-compliance is a continuous task and does not
end after construction. ROWs and licenses may
require renewal and modifications over the course of
the infrastructure’s lifespan, triggering evaluation of
potential impacts on critical habitat designated after
the initial ROW or license was approved. Existing
federal authorizations also may include provisions
requiring that consultation be re-initiated should new
critical habitat be designated that may be affected by
the authorized action. See 50 C.F.R. § 402.16(d)
(consultation must be reinitiated where federal discretionary involvement or control has been retained and
newly designated critical habitat may be affected).
Thus, there are several ways that existing energy
infrastructure could be affected by the designation of
areas that cannot sustain a species as “critical habitat”
for that species.
Critical habitat designations also can create
conflicts with other federal standards. For example,
the North American Electric Reliability Corporation
(“NERC”) requires vegetation management near regulated transmission lines to minimize risk of wildfires
and outages caused by vegetation contacting or
growing too close to lines. See NERC FAC-003-4,
Transmission Vegetation Management (October 1,
26
2016).
For similar reasons, utilities also practice
vegetation management near transmission and distribution lines that are not subject to NERC standards.
These required and voluntary vegetation management
activities may trigger ESA-related issues if the
vegetation along part of a route is within designated
critical habitat for a listed species. The activities
also may have a federal nexus such as a requirement
for a 404 permit or federal land management agency
approval prior to conducting vegetation management.
Desired vegetation conditions for the listed species
also may conflict with NERC requirements in some
cases. This could occur, for example, in riparian corridors where tall trees or shrubs could be an essential
feature of critical habitat for a listed species, yet
NERC standards may not allow taller vegetation near
regulated lines. To resolve the conflict between ESA
and NERC standards, the utility could be required to
conduct surveys to demonstrate species absence prior
to initiating work, comply with timing restrictions and
provide offsetting mitigation, even though – under the
criteria approved by the Fifth Circuit – the area is
unoccupied and uninhabitable by the species in question.
11
Finally, even where an EWAC member’s facility is
located entirely on private land and does not require
any federal permits (and therefore does not trigger the
obligations of ESA section 7(a)(2)), financing can be
adversely impacted if critical habitat occurs within or
adjacent to the facility’s footprint. Financiers will
often impose more expensive terms for financing based
on the existence of critical habitat because of the
potential that a future federal authorization or permit
11
NERC standard FAC-003-4 is available at: https://www.
nerc.com/pa/Stand/Reliability%20Standards/FAC-003-4.pdf.
27
could be needed, triggering ESA section 7 consultation, resulting in unanticipated costs.
Ultimately, the increased development and operating costs and the impacts of project delays connected
to critical habitat for listed species are borne by
electric power producers, consumers and taxpayers.
Even entirely private projects suffer economic consequences from critical habitat, through adverse impacts
on private financing.
C. Energy project developers seek to
avoid or minimize the impact of new
electricity generation, transmission,
and distribution infrastructure within
critical habitat.
In the interest of being good stewards of natural
resources, and recognizing the additional costs and
delays that are likely to result from siting projects in
critical habitat, EWAC’s members generally seek to
avoid affecting critical habitat and to minimize those
impacts that are unavoidable. Electricity generation
locations and transmission routes are carefully
examined, weighing a host of factors that routinely
include avoiding and minimizing impacts to sensitive
habitats and other natural resources. Indeed, EWAC
members often go to great lengths to purposely route
and site facilities in unoccupied (and uninhabitable)
and often degraded areas, specifically to avoid conflicts
with listed species and their habitat.
If routes or potential sites cannot avoid areas containing listed species or critical habitat, then potential
impacts on those areas can be evaluated, minimized,
and mitigated. During project design and ESA
consultation the effects on critical habitat often are
roughly estimated based on critical habitat maps.
28
This initial screening process is typically done at a
coarse scale, particularly because electric transmission and distribution systems extend over great
distances.
The wind energy industry developed, in coordination with the Service and other stakeholders, the
Land-Based Wind Energy Guidelines (“Guidelines”).12
These Guidelines recommend a tiered approach to
wind energy development starting first at landscape
scale site-screening and proceeding with each tier to
more site-specific data collection such as wildlife
surveys. This process is designed to screen out potential sites where impacts on species of concern cannot
be mitigated. See Guidelines at 9 (General Framework
of Tiered Approach). Similarly, transmission and distribution companies follow internal siting procedures
to identify and address potential impacts and to
optimize the time and cost to build a route.
The result of the screening process is that EWAC
members can and often do design and plan facilities to
avoid or minimize impacts to areas known to support
listed species, including occupied and unoccupied
critical habitat. For example, a transmission line or
wind or solar energy facility may be sited, when
feasible, to avoid wooded areas that are suitable for
listed bat species or riparian habitat that supports
listed salamanders. Once decisions are made about
routes and facility locations, it normally takes several
years to acquire or access property, obtain permits,
and construct the facilities. Many of the required
steps for developing a project hinge on site-specific
12
U.S. Fish & Wildlife Service, Land-Based Wind Energy
Guidelines (March 23, 2012), available at: https://www.fws.gov/
ecological-services/es-library/pdfs/WEG_final.pdf.
29
characteristics and land use requirements. Decisions
regarding facility siting and route selection, including
design changes, rerouting a segment or relocating
facilities, become increasingly expensive and challenging to revisit as the multi-year development process
proceeds.
D. Extending ESA “critical habitat” protection to lands that cannot sustain a
listed species threatens to disrupt the
development and operation of the
nation’s energy infrastructure.
If the Service can designate areas that are
uninhabitable by a listed species as “critical habitat”
subject to all of the protections of the ESA, that
impacts the development, operation, and maintenance
of the nation’s energy infrastructure. Further, all of
the care a project proponent takes to avoid sensitive
habitats will be for naught if the Service can interject,
at any point in the development timeline, a determination that lands that do not contain the physical or
biological features necessary to sustain an ESA-listed
species nevertheless are “unoccupied critical habitat”
and subject to the full protections afforded by the ESA.
Similar pressures come to bear on operating facilities. The designation of “unoccupied critical habitat”
within the footprint of an existing wind or solar energy
facility or overlapping the route of existing transmission
or distribution lines is likely to impose unanticipated
costs and may force changes in operation and maintenance practices. In addition to the impact on normal
operations of the facilities, it is routine for changes
to be made to existing facilities during their long
operating lives, and those changes can trigger the
same federal nexus as a new project. Designating
uninhabitable areas as “critical habitat” for a listed
30
species can disrupt those projects in a myriad of ways.
A project developer or facility operator simply cannot
anticipate or develop contingencies for the entirely
unpredictable risk that land which is not habitable by
a listed species can nevertheless be declared by the
Service to be “critical habitat,” with attendant regulatory consequences.
Returning to the example of the Corps-issued NWP
discussed in Section II.B. above, if the Service can
designate unsuitable, and indeed uninhabitable, land
as critical habitat, then the frequency with which the
notification requirements of the NWP’s General
Condition 18 are triggered will increase drastically.
Furthermore, these areas would have no distinguishable characteristics indicating they may support a
particular species, making it impossible for project
proponents to plan ahead to avoid certain areas since
anything could be fair game for a critical habitat
designation. For example, consider a wind energy
project with a layout carefully designed to avoid
woodland habitat that may be suitable for listed bat
species and has access road crossings requiring NWP
authorization from the Corps. If the project is sited on
former woodlands that were logged long ago and
converted to other uses, it would suddenly be at risk if
the Service were allowed to designate its site as
“unoccupied critical habitat” on the premise that the
land could one day revert back to forest and grow into
suitable bat habitat. Under this scenario, even though
the stream crossing regulated by the Corps is outside
the newly designated critical habitat, if the project has
not yet begun construction then the Corps could be
forced to reinitiate consultation, as the Service’s
expansive review could extend to effects on the former
woodlands where turbines will be located. See Section
7 Consultation Handbook at 4-17 – 4-18; 50 C.F.R.
31
§ 402.16(d) (consultation must be reinitiated where
federal discretionary involvement or control has been
retained and newly designated critical habitat may be
affected).
Or consider the transmission line route that
carefully avoided salamander habitat on federal lands.
If the Service later designated critical habitat near
streams that have been converted from native vegetation to agriculture but could, in theory, one day be
restored to support listed salamanders, the route could
suddenly be subject to section 7(a)(2) requirements for
any subsequent discretionary federal actions.
In both cases, infrastructure that had been sited
with the specific objective of avoiding sensitive habitat
suddenly and unexpectedly would overlap critical
habitat. There is no way the project developer could
anticipate that this could or would occur, potentially
years into the development process or after the project
has been constructed and begun operating. No preconstruction survey could reliably identify or quantify
this risk and any attempt to do so would be a highly
speculative, likely inaccurate and costly guess.
It becomes that much harder (indeed, nearly impossible) for all parties to evaluate future financial risk if
the Service has the power to designate land where a
project has been proposed or that is occupied by an
existing facility as critical habitat even though the
land lacks the physical or biological features needed to
sustain the listed species. Project developers would no
longer be assured of any benefit from avoiding the
habitat of listed species in favor of uninhabited and
uninhabitable areas. EWAC members simply could
not factor such possibilities into their siting and
routing decisions and it would be extremely difficult
for them to budget for these uncertainties. This affects
32
not only the potential cost of project development, but
also the designation of critical habitat affecting an
existing project also can be expected to increase its
operating costs. As noted in prior sections, these
increased costs are likely to be passed on to electricity
consumers in the form of higher rates, although for
electrical generation projects that are operating under
long-term power purchase agreements the costs may
be unrecoverable by the facility owner.
Moreover, as the Service and the Fifth Circuit
recognized, the designation of critical habitat could
decrease the asset value of any affected electrical
infrastructure, due to the stigma of the facility having
new, and likely undefined, obligations due to the new
critical habitat designation. See Pet. App. 13a (“a
property that is designated as critical habitat may
have a lower market value than an identical property
that is not within the boundaries of critical habitat due
to perceived limitations or restrictions.”). It could
devalue properties where assets have been retired or
are proposed for retirement, as well as land that was
purchased in anticipation of future needs and is
offered for sale when plans change.
These outcomes are unreasonable, as they will cause
delay and increase costs and could prevent projects
from being built or maintenance of existing infrastructure, disrupting access to reliable and affordable
electric power, all while providing little or no benefit
for listed species.
33
CONCLUSION
For the foregoing reasons, the judgment of the Court
of Appeals for the Fifth Circuit should be reversed.
Respectfully submitted,
STEVEN P. QUARLES
NOSSAMAN LLP
1666 K Street, NW
Suite 500
Washington, D.C. 20006
(202) 887-1400
BROOKE M. WAHLBERG
NOSSAMAN LLP
816 Congress Avenue
Suite 970
Austin, TX 78701
(512) 651-0660
SVEND A. BRANDT-ERICHSEN
Counsel of Record
NOSSAMAN LLP
601 Union Street
Suite 5305
Seattle, WA 98102
(206) 395-7632
sbrandterichsen@nossaman.com
Counsel for Amicus Curiae Energy and
Wildlife Action Coalition
April 30, 2018
This is a copy of a public record, reproduced as it was published. It is not legal advice, and it may not be the version a court would rely on. Check the official source before you cite it.