Amicus Curiae Brief — County of Maui, Hawaii, Petitioner v. Hawaii Wildlife Fund, et al.
Supreme Court briefMay 15, 2019
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No. 18-260
IN THE
Supreme Court of the United States
————
COUNTY OF MAUI,
Petitioner,
v.
HAWAI’I WILDLIFE FUND, ET AL.,
Respondents.
————
On Writ of Certiorari
to the United States Court of Appeals
for the Ninth Circuit
————
BRIEF OF AMICUS CURIAE CHAMBER OF
COMMERCE OF THE UNITED STATES OF AMERICA
SUPPORTING PETITIONER
————
STEVEN P. LEHOTSKY
AARON M. STREETT
MICHAEL B. SCHON
Counsel of Record
U.S. CHAMBER LITIGATION J. MARK LITTLE
CENTER
BAKER BOTTS L.L.P.
1615 H St., NW
910 Louisiana St.
Washington, D.C. 20062
Houston, TX 77002
(202) 659-6000
(713) 229-1234
aaron.streett@bakerbotts.com
Counsel for Amicus Curiae Chamber of
Commerce of the United States of America
WILSON-EPES PRINTING CO., INC. – (202) 789-0096 – WASHINGTON, D.C. 20002
i
QUESTION PRESENTED
Whether the CWA requires a permit when pollutants
originate from a point source but are conveyed to
navigable waters by a nonpoint source, such as
groundwater.
ii
TABLE OF CONTENTS
Page
Question Presented ............................................................... i
Interest Of Amicus Curiae ................................................. 1
Summary Of Argument ....................................................... 2
Argument .............................................................................. 3
I.
The Decision Below Overlooks Congressional
Limits On Federal CWA Authority And The
Existing State And Federal Regulatory
Regimes Governing Groundwater ............................ 3
II. The Ninth Circuit’s Expansion Of The Clean
Water Act Creates Significant Uncertainty ............ 8
III. The Court’s Rejection Of A Similar NonLegislative Expansion Of Regulatory Authority
In UARG Compels The Same Result Here ........... 13
Conclusion ........................................................................... 14
iii
TABLE OF AUTHORITIES
Page
CASES
FDA v. Brown & Williamson Tobacco
Corp.,
529 U.S. 120 (2000) ............................................13, 14
Sackett v. EPA,
566 U.S. 120 (2012) ................................................... 8
U.S. Army Corps of Eng’rs v. Hawkes
Co.,
136 S. Ct. 1807 (2016) .................................... 9, 10, 11
Util. Air Regulatory Grp. v. EPA,
573 U.S. 302 (2014) ............................................13, 14
FEDERAL STATUTES
33 U.S.C. § 1252(a) ......................................................... 3
33 U.S.C. § 1254(a)(5) ..................................................... 3
33 U.S.C. § 1311 .........................................................3, 10
33 U.S.C. § 1362 .....................................................3, 8, 10
33 U.S.C. § 2701 .............................................................. 7
42 U.S.C. §§ 300h-300h-8 ............................................... 7
42 U.S.C. § 6902 .............................................................. 6
42 U.S.C. § 6911 .............................................................. 6
42 U.S.C. § 6944 .............................................................. 6
42 U.S.C. § 9601 ...........................................................6, 7
42 U.S.C. § 9604 .............................................................. 6
FEDERAL REGULATIONS
40 C.F.R. § 122.44(i) ..................................................... 10
40 C.F.R. pt. 144 ............................................................. 7
iv
TABLE OF AUTHORITIES—Continued
Page
40 C.F.R. §§ 257.90-.98................................................... 7
40 C.F.R. §§ 258.50-.58................................................... 7
40 C.F.R. § 261.4(b)(5) ................................................... 7
40 C.F.R. § 300.430(a)(iii)(F) ......................................... 6
84 Fed. Reg. 16,810 (Apr. 23, 2019) ........................4, 14
STATE STATUTES
Ala. Code § 22-22-9(I)(3) ................................................ 5
Alaska Stat. Ann. § 46.03.710 ........................................ 5
Ariz. Rev. Stat. Ann. § 49-221 ....................................... 5
Ariz. Rev. Stat. Ann. § 49-241 ....................................... 5
Ariz. Rev. Stat. Ann. § 49-263 ....................................... 5
Ark. Code Ann. § 8-4-217 ............................................... 5
Cal. Water Code § 13260(a)(1) ...................................... 5
Cal. Water Code § 13304(a) ........................................... 5
Conn. Gen. Stat. Ann. § 22a-427 ................................... 5
Conn. Gen. Stat. Ann. § 22a-430 ................................... 5
D.C. Code Ann. § 8-103.02 ............................................. 5
Del. Code Ann. tit. 7, § 6003(a)...................................... 5
Fla. Stat. Ann. § 403.088(1) ........................................... 5
Fla. Stat. Ann. § 403.161(1) ........................................... 5
Ga. Code Ann. § 12-5-30 ................................................. 5
Haw. Rev. Stat. Ann. § 340E-2 ..................................... 7
Haw. Rev. Stat. Ann. § 342D-50.................................... 5
Idaho Code Ann. § 39-3618 ............................................ 5
Idaho Code Ann. § 39-3620 ............................................ 5
v
TABLE OF AUTHORITIES—Continued
Page
415 Ill. Comp. Stat. Ann. 5/12........................................ 5
Ind. Code Ann. § 13-18-4-5 ............................................ 5
Iowa Code Ann. § 455B.186 ........................................... 5
Kan. Stat. Ann. § 65-164 ................................................ 5
Ky. Rev. Stat. Ann. §§ 224.70-.110 ................................ 5
La. Stat. Ann. § 30:2075 ................................................. 5
La. Stat. Ann. § 30:2076 ................................................. 5
Me. Rev. Stat. tit. 38, § 413 ............................................ 5
Md. Code Ann., Envir. § 9-322 ...................................... 5
Mass. Gen. Laws Ann. ch. 21, § 42 ................................ 5
Mass. Gen. Laws Ann. ch. 21, § 43 ................................ 5
Mich. Comp. Laws Ann. § 324.3109(1) ......................... 5
Minn. Stat. Ann. § 115.061 ............................................. 5
Miss. Code Ann. § 49-17-29(2)(a) .................................. 5
Mo. Ann. Stat. § 644.051 ................................................ 5
Mont. Code Ann. § 75-5-605 .......................................... 5
Neb. Rev. Stat. Ann. § 81-1506 ..................................... 5
Nev. Rev. Stat. Ann. § 445A.570 ................................... 5
N.H. Rev. Stat. Ann. § 485-A:12 ................................... 5
N.H. Rev. Stat. Ann. § 485-A:13 ................................... 5
N.J. Stat. Ann. § 58:10A-6 ............................................. 5
N.M. Stat. Ann. § 74-6-4 ................................................ 5
N.Y. Envtl. Conserv. Law § 17-0501 ............................ 5
N.C. Gen. Stat. Ann. § 143-215.1(a)(6) ......................... 5
Ohio Rev. Code Ann. § 6111.04 ..................................... 5
vi
TABLE OF AUTHORITIES—Continued
Page
Okla. Stat. Ann. tit. 27A, § 2-6-105................................ 5
Or. Rev. Stat. Ann. § 468B.025(1) ................................. 5
25 Pa. Code § 93.8a(a) .................................................... 5
46 R.I. Gen. Laws Ann. § 46-12-5 ................................. 5
S.C. Code Ann. § 48-1-90(A)(1) ..................................... 5
S.D. Codified Laws § 34A-2-21 ..................................... 5
S.D. Codified Laws § 34A-2-22 ..................................... 5
Tenn. Code Ann. § 69-3-108(b) ...................................... 5
Tex. Water Code Ann. § 26.001(5) ................................ 4
Tex. Water Code Ann. § 26.121(a) ................................ 4
Utah Code Ann. § 19-5-107(1) ....................................... 5
Vt. Stat. Ann. tit. 10, § 1259 ........................................... 5
Va. Code Ann. § 62.1-44.5(A) ......................................... 5
Va. Code Ann. § 62.1-194.1 ............................................ 5
Wash. Rev. Code § 90.48.080 ......................................... 5
Wash. Rev. Code § 90.48.160 ......................................... 5
W. Va. Code Ann. § 22-11-8 ........................................... 5
Wis. Stat. Ann. § 281.19(1) ............................................. 5
Wis. Stat. Ann. § 281.20(1)(a) ........................................ 5
Wyo. Stat. Ann. § 35-11-301 .......................................... 5
STATE REGULATIONS
5 Colo. Code Regs. § 1002-61:61.3 ................................ 5
Haw. Code R. § 11-23-06 ................................................ 7
Haw. Code R. § 11-23-07 ................................................ 7
Idaho Admin. Code r. 58.01.11.400 ............................... 5
vii
TABLE OF AUTHORITIES—Continued
Page
Mich. Admin. Code r. 323.2201(i) .................................. 5
Mich. Admin. Code r. 323.2204-05 ................................ 5
Minn. R. 7050.0210 ......................................................... 5
Nev. Admin. Code 445A.228 .......................................... 5
N.M. Admin. Code 20.6.2.1201 ...................................... 5
N.M. Admin. Code 20.6.2.3104 ...................................... 5
30 Tex. Admin. Code §§ 350.1-.135 ............................... 4
30 Tex. Admin. Code § 350.32 ....................................... 5
30 Tex. Admin. Code § 350.33 ....................................... 5
30 Tex. Admin. Code § 350.52 ....................................... 5
30 Tex. Admin. Code § 350.75(i) .................................... 5
OTHER AUTHORITIES
EPA, ICR Supporting Statement, Information Collection Request for National
Pollutant Discharge Elimination System (NPDES) Program (Renewal),
OMB Control No. 2040-0004, EPA ICR
No. 0229.22 (Sept. 2017) ........................................ 12
EPA, NPDES Permit Writer’s Manual,
EPA-833-K-10-001 (Sept. 2010)...................... 10, 11
EPA, Summary of Key Existing EPA
CERCLA Policies for Groundwater
Restoration, OSWER Directive 9283.133 (June 26, 2009) ..................................................... 6
EPA, Superfund Groundwater Guidance
and Reports .............................................................. 6
viii
TABLE OF AUTHORITIES—Continued
Page
Legislative History of the Resource
Conservation and Recovery Act of 1976
P.L. 94-580, Report to Congress by the
EPA Pursuant to Section 212 of the
Solid Waste Disposal Act, As Amended
(June 1974) ................................................................ 6
IN THE
Supreme Court of the United States
————
NO. 18-260
————
COUNTY OF MAUI,
Petitioner,
v.
HAWAI’I WILDLIFE FUND, ET AL.,
Respondents.
————
On Writ of Certiorari
to the United States Court of Appeals
for the Ninth Circuit
————
BRIEF OF AMICUS CURIAE CHAMBER OF
COMMERCE OF THE UNITED STATES OF AMERICA
SUPPORTING PETITIONER
————
INTEREST OF AMICUS CURIAE1
Amicus curiae the Chamber of Commerce of the
United States of America (the Chamber) is the world’s
largest business federation. It represents 300,000 direct
members and indirectly represents the interests of more
than three million companies and professional organizations of every size, in every industry sector, and from
every region of the country. An important function of the
Petitioner’s counsel of record consented to the filing of this brief.
Respondents’ counsel of record has filed a blanket consent to all amicus briefs. In accordance with this Court’s Rule 37.6, no counsel for
any party has authored this brief in whole or in part, and no person
or entity, other than amicus, its members, or its counsel, have made
a monetary contribution to the preparation or submission of this
brief.
1
2
Chamber is to represent the interests of its members in
matters before Congress, the Executive Branch, and the
courts. To that end, the Chamber regularly files amicus
curiae briefs in cases such as this one that raise issues of
concern to the Nation’s business community.
The Ninth Circuit’s breathtaking expansion of the
CWA’s National Pollutant Discharge Elimination System
(NPDES) permitting program to cover groundwater
threatens interests of great importance to the Chamber’s
members. The business community supports safe, effective, and efficient environmental regulation. The decision
below imperils these objectives. Indeed, applying the
CWA to point sources that convey pollutants to groundwater—an area already extensively regulated by other
state and federal programs—will create a morass of duplicative and potentially conflicting regulation. The regulatory uncertainty and vastly increased compliance costs
that will follow this sea change in CWA law will impose
substantial burdens on the regulated public that Congress never intended.
SUMMARY OF ARGUMENT
Congress drew a clear line limiting the scope of federal permitting and enforcement under the CWA’s point
source permitting program. The program covers discharges from point sources into navigable waters. Other
releases, including those that reach navigable waters
through nonpoint sources like groundwater, are already
covered by an array of other state and federal laws. The
court of appeals’ expansion of the CWA disrupts that established framework by adding groundwater regulation
into a statutory program that was never designed to regulate groundwater.
Forcing the square peg of groundwater regulation into
the round hole of the CWA’s point source permitting
program promises dire and far-reaching consequences.
3
It is a recipe for regulatory uncertainty, wasteful overlap,
and unpredictable compliance costs. Those effects will be
felt by myriad businesses, individuals, and the Nation as
a whole.
The Court has consistently rejected similarly transformative regulatory expansions without clear Congressional authorization. It has been rightly skeptical of
agencies’ efforts to uncover such authorization lying
dormant in long-extant statutes. The Ninth Circuit’s
strained application of the CWA’s point source provisions
to groundwater—which comes over four decades after
the statute’s enactment—merits the same treatment.
What is more, unlike in some of the Court’s previous decisions that refused similar expansions, no agency deference applies to the Ninth Circuit’s disruptive interpretation. To the contrary, the Environmental Protection
Agency (EPA) has expressly rejected the Ninth Circuit’s
expansion of the statute.
ARGUMENT
I.
THE DECISION BELOW OVERLOOKS CONGRESSIONAL LIMITS ON FEDERAL CWA AUTHORITY AND THE
EXISTING STATE AND FEDERAL REGULATORY REGIMES GOVERNING GROUNDWATER
A. Congress purposefully limited the federal government’s CWA NPDES authority to discharges to “navigable waters.” 33 U.S.C. §§ 1311, 1362(12). Before the
law’s enactment, EPA asked Congress for authority to
regulate discharges to groundwater under the CWA
point source program in order to prevent polluted
groundwater from harming surface waters. See Pet. Br.
40-41. Congress rejected that request, id., and the CWA
plainly differentiates between jurisdictional “navigable
waters” and “ground waters.” 33 U.S.C. §§ 1252(a),
1254(a)(5).
4
The opinion below creates a new standard out of whole
cloth, applying NPDES point source permitting requirements to releases of pollutants into groundwater if
the “pollutants are fairly traceable from the point source
to a navigable water” and reach navigable water at “more
than de minimis” levels. Pet. App. 24. That test finds no
footing whatsoever in the statutory text. Indeed, it ignores the CWA’s considered statutory distinction by allowing—and indeed requiring—federal regulation of not
just “navigable waters,” but of groundwater as well.
Nor does the Ninth Circuit’s expansion of the CWA
plug some inadvertent regulatory gap. The point source
permitting program’s focus on “navigable waters” instead reflects Congress’s recognition that numerous other state and federal regulatory programs have been developed to protect groundwater. Thus, as EPA recently
observed, “[t]here is sufficient legal authority to address
releases of pollutants to groundwater that subsequently
reach jurisdictional surface waters at both the state and
federal level without expanding the CWA’s regulatory
reach beyond what Congress envisioned.” 84 Fed. Reg.
16,810, 16,823 (Apr. 23, 2019).
B. All fifty states exercise broad police powers to
protect their groundwater from pollution. To take one
representative example, Texas has implemented a permitting regime overseen by the Texas Commission on
Environmental Quality. Without a permit, it is illegal to
“discharge sewage, municipal waste, recreational waste,
agricultural waste, or industrial waste into or adjacent to
any water in the state,” including “groundwater.” Tex.
Water Code Ann. §§ 26.001(5), 26.121(a). The Texas Risk
Reduction Program further safeguards Texas groundwater. See 30 Tex. Admin. Code §§ 350.1-.135. That comprehensive program provides for investigation and remediation of contaminated sites within the state and includes measures specifically designed for groundwater
5
contamination. See, e.g., id. §§ 350.32-.33 (providing remedial standards for groundwater); id. § 350.52 (establishing a “groundwater resource classification system”);
id. § 350.75(i) (including groundwater-to-surface-water
pathway in remediation framework). The other fortynine states employ similar regulatory regimes to protect
their groundwater.2
C. While Congress did not apply the CWA’s strict liability permitting regime to releases into groundwater, it
did address specific groundwater concerns in other parts
See Ala. Code § 22-22-9(I)(3); Alaska Stat. Ann. § 46.03.710; Ariz.
Rev. Stat. Ann. §§ 49-221, 49-241, 49-263; Ark. Code Ann. § 8-4-217;
Cal. Water Code §§ 13260(a)(1), 13304(a); 5 Colo. Code Regs. § 100261:61.3; Conn. Gen. Stat. Ann. §§ 22a-427, 22a-430; Del. Code Ann.
tit. 7, § 6003(a); D.C. Code Ann. § 8-103.02; Fla. Stat. Ann.
§§ 403.088(1), 403.161(1); Ga. Code Ann. § 12-5-30; Haw. Rev. Stat.
Ann. § 342D-50; Idaho Code Ann. §§ 39-3618, 39-3620; Idaho Admin.
Code r. 58.01.11.400; 415 Ill. Comp. Stat. Ann. 5/12; Ind. Code Ann.
§ 13-18-4-5; Iowa Code Ann. § 455B.186; Kan. Stat. Ann. § 65-164;
Ky. Rev. Stat. Ann. §§ 224.70-.110; La. Stat. Ann. §§ 30:2075,
30:2076; Me. Rev. Stat. tit. 38, § 413; Md. Code Ann., Envir. § 9-322;
Mass. Gen. Laws Ann. ch. 21, §§ 42-43; Mich. Comp. Laws Ann.
§ 324.3109(1); Mich. Admin. Code r. 323.2201(i), 323.2204-05; Minn.
Stat. Ann. § 115.061; Minn. R. 7050.0210; Miss. Code Ann. § 49-1729(2)(a); Mo. Ann. Stat. § 644.051; Mont. Code Ann. § 75-5-605; Neb.
Rev. Stat. Ann. § 81-1506; Nev. Rev. Stat. Ann. § 445A.570; Nev.
Admin. Code 445A.228; N.H. Rev. Stat. Ann. §§ 485-A:12, 485-A:13;
N.J. Stat. Ann. § 58:10A-6; N.M. Stat. Ann. § 74-6-4; N.M. Admin.
Code 20.6.2.1201, 20.6.2.3104; N.Y. Envtl. Conserv. Law § 17-0501;
N.C. Gen. Stat. Ann. § 143-215.1(a)(6); N.D. Cent. Code Ann. § 61-2806; Ohio Rev. Code Ann. § 6111.04; Okla. Stat. Ann. tit. 27A, § 2-6105; Or. Rev. Stat. Ann. § 468B.025(1); 35 Pa. Stat. Ann. § 691.401; 25
Pa. Code § 93.8a(a); 46 R.I. Gen. Laws Ann. § 46-12-5; S.C. Code
Ann. § 48-1-90(A)(1); S.D. Codified Laws §§ 34A-2-21, 34A-2-22;
Tenn. Code Ann. § 69-3-108(b); Utah Code Ann. § 19-5-107(1); Vt.
Stat. Ann. tit. 10, § 1259; Va. Code Ann. §§ 62.1-44.5(A), 62.1-194.1;
Wash. Rev. Code §§ 90.48.080, 90.48.160; W. Va. Code Ann. § 22-11-8;
Wis. Stat. Ann. §§ 281.19(1), 281.20(1)(a); Wyo. Stat. Ann. § 35-11301.
2
6
of the CWA and in other federal statutes. For example,
the
Comprehensive
Environmental
Response,
Compensation, and Liability Act (CERCLA) empowers
EPA to remedy the “release” of any “hazardous substance” and certain other “pollutants” into the “environment,” a term that specifically includes “ground water.”
42 U.S.C. §§ 9601(8), 9604(a)(1). Indeed, EPA has developed principles to direct its efforts in this area and maintains a vast store of groundwater guidance, reports, and
tools for its Superfund Remedial Project Managers. See
EPA, Summary of Key Existing EPA CERCLA Policies
for Groundwater Restoration, OSWER Directive 9283.133 (June 26, 2009);3 EPA, Superfund Groundwater Guidance and Reports.4 For example, the National Oil and
Hazardous Substance Pollution Contingency Plan, which
provides the blueprint for CERCLA implementation,
states that “EPA expects to return usable ground waters
to their beneficial uses wherever practicable.” 40 C.F.R.
§ 300.430(a)(iii)(F).
The Resource Conservation and Recovery Act
(RCRA), moreover, provides EPA with specific powers
over groundwater contamination that results from solid
waste disposal. See 42 U.S.C. §§ 6902, 6911, 6944.
RCRA was motivated in part when EPA alerted Congress of the need to fill gaps in the CWA’s coverage regarding “pollutant discharges normally associated with
improperly managed hazardous waste disposal facilities”
and their “migration into groundwater supplies.”
Legislative History of the Resource Conservation and
Recovery Act of 1976 P.L. 94-580, Report to Congress by
the EPA Pursuant to Section 212 of the Solid Waste
Disposal Act, As Amended 19 (June 1974). Under
https://semspub.epa.gov/work/HQ/175202.pdf.
https://www.epa.gov/superfund/superfund-groundwater-guidanceand-reports.
3
4
7
RCRA, EPA has promulgated regulations protecting
groundwater, including a comprehensive program that
provides for monitoring and remediation of groundwater
affected by certain waste treatment and storage facilities.
See 40 C.F.R. §§ 257.90-.98, 258.50-.58.5
The Safe Drinking Water Act (SDWA) also includes
extensive provisions to ensure the safety of “underground sources of drinking water.” 42 U.S.C. §§ 300h300h-8. The SDWA specifically focuses on the dangers
posed by injection wells. It establishes a regulatory
structure to protect groundwater from that type of contamination. Ibid.
D. The injection wells at issue in this case fall within
the scope of both state and federal regulatory regimes
protecting groundwater. On the state side, the wells had
to comply with the requirements of Hawai’i’s safe drinking water program, see Haw. Rev. Stat. Ann. § 340E-2,
which has regulations specifically designed for these
types of injection wells, see Haw. Code R. §§ 11-23-06,
11-23-07. Federally, EPA regulates these types of injection wells pursuant to its authority under the SDWA and
has promulgated regulations designed to prevent contamination from such wells. See 40 C.F.R. pt. 144. It is
undisputed that the County of Maui obtained all necessary permits under both state and federal programs.
CERCLA and RCRA both exclude certain types of petroleum and
drilling materials from their scope. See 42 U.S.C. § 9601(14) (CERCLA excluding “petroleum, including crude oil or any fraction thereof which is not otherwise specifically listed or designated as a hazardous substance”); 40 C.F.R. § 261.4(b)(5) (excluding from RCRA’s
definition of hazardous waste “[d]rilling fluids, produced waters, and
other wastes associated with the exploration, development, or production of crude oil, natural gas or geothermal energy”). But the
statutes nonetheless have broad coverage, and other state and federal regulatory programs, such as the one created by the Oil Pollution Act, 33 U.S.C. § 2701 et seq., ably fill any gaps.
5
8
In short, the states and the federal government are already extensively regulating groundwater—and even the
very injection wells at issue in this case. There was no
need for the Ninth Circuit to stretch the CWA NPDES
permit program to cover this area. And doing so promises duplicative and costly groundwater regulation.
II. THE NINTH CIRCUIT’S EXPANSION OF THE CLEAN
WATER ACT CREATES SIGNIFICANT UNCERTAINTY
“[C]larity and predictability” are critical in the CWA
context because the combination of an “uncertain reach
of the Clean Water Act and the draconian penalties imposed for * * * violations” cannot be tolerated. Sackett v.
EPA, 566 U.S. 120, 132-133 (2012) (Alito, J., concurring).
The regulatory chaos that would follow if the decision below is upheld would create uncertainty and impose exorbitant costs on the public.
A. Under the court of appeals’ decision, regulated individuals and entities will be forced to navigate a labyrinth of rules with pitfalls at every turn. The first question they face is whether a given activity that may affect
groundwater now requires a point source permit. The
potential reach of the decision below is sweeping. One
reason is that the CWA’s definition of “pollutant” is extremely broad. That term includes “dredged spoil, solid
waste, incinerator residue, sewage, garbage, sewage
sludge, munitions, chemical wastes, biological materials,
radioactive materials, heat, wrecked or discarded equipment, rock, sand, cellar dirt and industrial, municipal,
and agricultural waste discharged into water.” 33 U.S.C.
§ 1362(6). Thus, any release of “rock,” “sand,” or even
“heat[ed]” water into groundwater could potentially fall
within the Ninth Circuit’s expanded point source program.
The court of appeals’ standard, paired with this broad
definition of “pollutant,” could encompass a wide swath of
9
activities. Septic systems—both large commercial ones
and the ubiquitous personal ones that dot rural America—could qualify, requiring a federal permit and federal
oversight at countless private properties. Municipal
storm sewers, brownfield cleanup sites, and other locations already covered by other federal and state regulatory regimes could also enter the point source program’s
crosshairs. Various kinds of basins and impoundments,
like those employed in agricultural operations or for
stormwater control, could face CWA regulation under
this judicially expanded version of the statute as well, if
they employ infrastructure that qualifies as a point
source. And that is just the beginning of a much longer
list, for it takes little creativity to describe a host of personal and commercial activities as “fairly traceable” to
“more than de minimis” impacts on groundwater.
Moreover, to avoid the “crushing” penalties levied for
even “inadvertent” unpermitted discharges, U.S. Army
Corps of Eng’rs v. Hawkes Co., 136 S. Ct. 1807, 1816
(2016) (Kennedy, J., concurring), every company and individual that is engaged in any of these activities must
determine: (1) whether their activities could qualify as a
point source; (2) if so, whether any pollutants that migrate through the groundwater to navigable waters are
“fairly traceable” to their releases; and (3) whether those
pollutants reach navigable waters at “more than de minimis” levels. Determining whether a particular release
into groundwater meets the latter two of those elements
will require hiring experts to conduct a complicated analysis to assess the level of hydrological connectivity between the particular body of groundwater and a specific
body of surface water. Both sophisticated commercial
enterprises and rural residents alike will have to bear the
steep financial cost of such an analysis because it is the
only way to determine whether activity that affects
groundwater comes within the CWA point source pro-
10
gram’s expanded scope. To make matters worse, because
the science is imperfect and the “fairly traceable” and
“more than de minimis” standards are imprecise, even
the most conscientious actor will not obtain anything approaching certainty regarding whether he is subject to a
strict liability permitting regime that carries civil and
criminal penalties for noncompliance.
The regulated individual or entity’s task becomes even
more onerous after that initial step. If, for example, a
septic-system operator decides that the results of its
analysis are concerning enough to justify seeking a CWA
permit, it faces a daunting road ahead. Obtaining permits under the CWA is “arduous, expensive, and long” at
the best of times. Id. at 1815. The challenges confronting a groundwater applicant would be even more severe.
That is because the point source permitting program
is designed for discrete discharges into navigable waters.
It imposes “effluent limitations” on “discernible, confined
and discrete conveyance[s],” 33 U.S.C. §§ 1311, 1362(14),
and requires precise effluent measurement and monitoring. See generally EPA, NPDES Permit Writer’s Manual, EPA-833-K-10-001 (Sept. 2010) (“NPDES Permit
Writer’s Manual”).6 The types of measurements and
monitoring that the point source permitting program
demands are infeasible at best and impossible at worst in
the context of effluent that migrates through groundwater. For example, point source permittees are required
to measure the “mass * * * for each pollutant limited in
the permit” and the “volume of effluent discharged from
each outfall.” 40 C.F.R. § 122.44(i). Those requirements
make sense as applied to point sources that discharge into navigable waters. Sampling and monitoring of the effluent can occur at the pipe or channel that delivers it to
the body of surface water. See NPDES Permit Writer’s
6
https://www.epa.gov/npdes/npdes-permit-writers-manual.
11
Manual § 8.1.2 (providing guidelines for selecting a monitoring location). But that approach does not work for effluent that migrates through groundwater. There is no
pipe or channel from which to monitor and measure.
There is instead only a diffuse effluent flow from the
groundwater into navigable waters at some later point in
time. The measurement and monitoring regime that the
permitting program appropriately requires for point
sources simply does not fit the very different context
presented here. Consequently, the point source permitting program is poorly equipped to handle the flood of
groundwater permits that may soon inundate it.
Assuming our hypothetical operator somehow gets a
permit despite those difficulties, the cost of compliance
can also be prohibitive, particularly when viewed in conjunction with the compliance costs for the other federal,
state, and local regulatory programs that already protect
groundwater. And failure to obtain a permit could preclude land use or business operations and lead to “crushing” financial or even criminal penalties for unpermitted
discharges. Hawkes, 136 S. Ct. at 1816 (Kennedy, J.,
concurring).
Given the uncertainty inherent in this process and the
draconian penalties for releases that are later determined to have required a permit, risk-averse individuals
and businesses will often err on the side of caution and
seek a permit no matter the cost. The result will be a
wasteful allocation of significant resources into obtaining
thousands, if not millions, of NPDES permits that may
ultimately be unnecessary even under the Ninth Circuit’s
view.
Thus, at best, the Ninth Circuit’s interpretation would
force a host of new individuals and businesses to protectively seek burdensome and possibly duplicative CWA
permits. At worst, it would discourage and restrict environmentally sound practices.
12
B. Even before the decision below, the point source
permitting program imposed staggering costs in the pursuit of its laudable goals. According to EPA estimates,
the public spends over 26 million labor hours and over $1
billion annually in applying for and complying with point
source permits. EPA, ICR Supporting Statement, Information Collection Request for National Pollutant Discharge Elimination System (NPDES) Program (Renewal), OMB Control No. 2040-0004, EPA ICR No. 0229.22,
at 23, tbl. 12.1 (Sept. 2017).7 If the Ninth Circuit’s dramatically expanded version of the program stands, those
costs can be expected to rise exponentially. And that is
before factoring in the opportunity costs of businesses
rejecting otherwise profitable and economically efficient
endeavors because of the newly added compliance costs
or the risk of inadvertent violations of the court of appeals’ amorphous standard.
It is the province of Congress to weigh these significant costs against any perceived gains from extending
the CWA’s point source program to groundwater, taking
into account existing federal and state protections. Congress has thus far determined that the costs and benefits
weigh against extending the point source program in that
manner. It is not the role of federal courts to secondguess Congress on that distinctly legislative choice. The
Court should restore the longstanding limits on the reach
of the CWA and its point source permitting program that
the statute’s text, intent, and history demand.
https://www.regulations.gov/document?D=EPA-HQ-OW-2008-071
9-0110.
7
13
III. THE COURT’S REJECTION OF A SIMILAR NONLEGISLATIVE EXPANSION OF REGULATORY AUTHORITY IN UARG COMPELS THE SAME RESULT
HERE
The Ninth Circuit’s extravagant extension of the CWA
also cannot stand because “it would bring about an enormous and transformative expansion in EPA’s regulatory
authority without clear congressional authorization.”
Util. Air Regulatory Grp. v. EPA (“UARG”), 573 U.S.
302, 324 (2014).
That is precisely the basis on which this Court rejected a similarly disruptive interpretation of the Clean Air
Act in UARG. At issue was EPA’s claim that it possessed the theretofore unrecognized “power to require
permits for the construction and modification of tens of
thousands, and the operation of millions, of small sources
nationwide” because they emitted greenhouse gases.
Ibid. Despite applying the deferential Chevron framework, the Court ultimately rejected EPA’s reading of the
statute as unreasonable. Id. at 321. The Court explained
that “[w]hen an agency claims to discover in a longextant statute an unheralded power to regulate ‘a significant portion of the American economy,’ we typically greet
its announcement with a measure of skepticism.” Id. at
324 (quoting FDA v. Brown & Williamson Tobacco
Corp., 529 U.S. 120, 159 (2000)). Instead, the Court “expect[s] Congress to speak clearly if it wishes to assign to
an agency decisions of vast ‘economic and political significance.’” Ibid. (quoting Brown & Williamson, 529 U.S. at
160). Because Congress had not amended the Clean Air
Act to provide such a clear regulatory authorization to
EPA, the Court rejected EPA’s interpretation as unreasonable. See id. at 321-324.
That reasoning applies here. Much as in UARG, the
Ninth Circuit’s massive expansion of the CWA would
14
“radically transform th[e] [NPDES] program[] and render [it] unworkable.” Id. at 320. And in another parallel
to UARG, the claimed source for that new power to regulate “‘a significant portion of the American economy’” is a
“long-extant statute” that no court of appeals had previously read to extend to groundwater. Id. at 324 (quoting
Brown & Williamson, 529 U.S. at 159).
In stark contrast to UARG, however, no deference of
any kind attends the Ninth Circuit’s interpretation of the
CWA. Indeed, EPA has explicitly rejected the court of
appeals’ view of the statute, “conclud[ing] that the Act is
best read as excluding all releases of pollutants from a
point source to groundwater from NPDES program coverage and liability under [the point source provisions] of
the CWA, regardless of a hydrologic connection between
the groundwater and a jurisdictional surface water.” 84
Fed. Reg. 16810, 16810 (Apr. 23, 2019). Without the
counterweight of Chevron deference, UARG’s reasoning
applies with even greater force here.
CONCLUSION
The judgment of the court of appeals should be
reversed.
15
Respectfully submitted.
STEVEN P. LEHOTSKY
MICHAEL B. SCHON
U.S. CHAMBER LITIGATION
CENTER
1615 H St., NW
Washington, D.C. 20062
(202) 659-6000
AARON M. STREETT
Counsel of Record
J. MARK LITTLE
BAKER BOTTS L.L.P.
910 Louisiana St.
Houston, TX 77002
(713) 229-1234
aaron.streett@bakerbotts.com
Counsel for Amicus Curiae Chamber of
Commerce of the United States of America
May 2019
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.