Amicus Curiae Brief — County of Maui, Hawaii, Petitioner v. Hawaii Wildlife Fund, et al.

Supreme Court briefMay 16, 2019

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Text

No. 18-260

IN THE

Supreme Court of the United States

————

COUNTY OF MAUI,

Petitioner,

v.

HAWAI’I WILDLIFE FUND; SIERRA CLUB –

MAUI GROUP; SURFRIDER FOUNDATION;

WEST MAUI PRESERVATION ASSOCIATION,

Respondents.

————

On Writ of Certiorari to the

United States Court of Appeals

for the Ninth Circuit

————

BRIEF OF WYCHMERE SHORES

CONDOMINIUM TRUST AND LONGWOOD

VENUES & DESTINATIONS, INC. AS

AMICI CURIAE IN SUPPORT OF PETITIONER

————

KEVIN M. MCGINTY

Counsel of Record

JEFFREY R. PORTER

ANDREW NATHANSON

EMILY KANSTROOM MUSGRAVE

MINTZ, LEVIN, COHN, FERRIS,

GLOVSKY AND POPEO, P.C.

One Financial Center

Boston, MA 02111

(617) 542-6000

kmcginty@mintz.com

Counsel for Amici Curiae

May 16, 2019

WILSON-EPES PRINTING CO., INC. – (202) 789-0096 – WASHINGTON, D. C. 20002

TABLE OF CONTENTS

Page

TABLE OF AUTHORITIES ................................

ii

STATEMENT OF INTEREST OF

AMICI CURIAE ...............................................

1

SUMMARY OF ARGUMENT .............................

2

ARGUMENT ........................................................

4

I. Amici’s Circumstances Illustrate The

Extent To Which The HydrologicConnection Theory Will Expand The

Scope Of The NPDES Program ................

4

II. Adopting The Hydrologic-Connection

Theory Will Trigger A Broad Expansion

Of The NPDES Program And Threaten

The Interests Of Millions Of Parties Who

Have Historically Been Regulated By

The States .................................................

9

III. Rejecting The Hydrologic-Connection

Theory Is Consistent With The Express

Purpose Of The CWA, And Will Not

(As Some Have Claimed) Create A

“Loophole” Allowing The Unregulated

Pollution Of Navigable Waters ................

15

CONCLUSION ....................................................

21

(i)

ii

TABLE OF AUTHORITIES

CASES

Page(s)

Conservation Law Found. v. Longwood

Venues & Destinations, Inc. et al.,

No. 1:18-cv-11821-WGY (D. Mass. filed

Aug. 24, 2018).............................................

1

Exxon Corp. v. Train,

554 F.2d 1310 (5th Cir. 1977) ............. 11, 15, 16

Hawai’i Wildlife Fund v. Cty. of Maui,

886 F.3d 737 (9th Cir. 2018) ............. 6, 9, 12, 15

Kentucky Waterways All. v. Kentucky Utils. Co.,

905 F.3d 925 (6th Cir. 2018) .....................

16

Oregon Natural Desert Ass’n v.

United States Forest Serv.,

550 F.3d 778 (9th Cir. 2008) .....................

16

Tenn. Clean Water Network v.

Tenn. Valley Auth.,

905 F.3d 436 (6th Cir. 2018) .....................

16

Upper Blackstone Water Pollution

Abatement Dist. v. EPA,

690 F.3d 9 (1st Cir. 2012) .........................

8

Upstate Forever v. Kinder Morgan Energy

Partners, L.P.,

887 F.3d 637 (4th Cir. 2018) ........... 9, 10, 15–16

STATUTES AND REGULATIONS

33 U.S.C. § 1251 et seq .................................

19

§ 1251(b) (2011) ......................................... 14, 16

§ 1362(12) (2010) .......................................

12

iii

TABLE OF AUTHORITIES—Continued

Page(s)

310 Mass. Code Regs. 15.000 et seq. (2016) ...

19

314 Mass. Code Regs. 4.00 et seq. (2013) .....

19

4.01(4) (2013) ............................................

19

314 Mass. Code Regs. 5.00 et seq. (2016) .....

18

5.03 (2016) .................................................

18

5.05(1)(a) (2016) ........................................

18

5.10(3) (2016) ............................................ 19, 20

Mass. Clean Waters Act, Mass. Gen. Laws

ch. 21, § 26 .................................................

18

RULES

Fed. R. Civ. P. 34 ..........................................

8

COURT FILINGS

Am. Compl., Conservation Law Found. v.

Long-wood Venues & Destinations, Inc. et

al., No. 1:18-cv-11821-WGY (D. Mass.

filed March 12, 2019), ECF No. 34 ......... 2, 8, 10

Case Management Order, Conservation

Law Found. v. Longwood Venues &

Destinations, Inc. et al., No. 1:18-cv11821-WGY (D. Mass. Feb. 3, 2019), ECF

No. 30 ........................................................

8

Defs.’ Answer & Affirmative Defenses to

Pl.’s Am. Compl., Conservation Law Found.

v. Long-wood Venues & Destinations, Inc.

et al., No. 1:18-cv-11821-WGY (D. Mass.

Apr. 5, 2019), ECF No. 49.........................

5

iv

TABLE OF AUTHORITIES—Continued

Page(s)

Mem. in Supp. of Defs.’ Mot. to Dismiss,

Conservation Law Found. v. Longwood

Venues & Destinations, Inc. et al., No.

1:18-cv-11821-WGY (D. Mass. Nov. 30,

2018), ECF No. 16 .....................................

7

OTHER AUTHORITIES

Cape Cod Commission, Regional Wastewater Management Plan, http://www.

capecodcommission.org/regionalplans/RW

MP (last visited May 13, 2019).................

18

Cape Cod Commission, Wastewater, http://

www.capecodcommission.org/index.php?

id=170 (last visited May 10, 2019) ...........

10

Interpretive Statement on Application of

the Clean Water Act National Pollutant

Dis-charge Elimination System Program

to Releases of Pollutants from a Point

Source to Groundwater, 84 Fed. Reg.

16,810 (Apr. 23, 2019) ...............................

7

Marc R. Poirier, Non-point Source Pollution,

in Env. Practice Guide (2008) ...................

16

Mass. Dep’t of Env. Prot., Massachusetts

Non-point Source Management Program

Plan 2014–2019 (2014) .............................

18

Mass. Dep’t of Env. Prot., Total Maximum

Daily Load for Total Nitrogen in Wychmere

Harbor (Feb. 2016) ....................................

6

v

TABLE OF AUTHORITIES—Continued

Page(s)

NOAA, National Coastal Population

Report: Population Trends from 1970 to

2020 (Mar. 2013) .......................................

11

S. Rep. No. 414, 92d Cong., 1st Sess. 73

(1971), reprinted in 1972 U.S. Code Cong.

& Admin. News 3739 ................................ 16–17

U.S. Dep’t of Hous. & Urban Dev. & U.S.

Census Bureau, American Housing Survey

for the United States: 2011 (2013) ...........

10

U.S. Env. Prot. Agency, Decentralized

Systems Technology Fact Sheet: Septic

Tank Soil Absorption Systems (Sept.

1999), https://www.h-gac.com/community/

water/ossf/DSTFS_Septic-Tank_Soil-Abs

orption-Systems.pdf .................................. 12, 13

STATEMENT OF INTEREST OF AMICI CURIAE1

Wychmere Shores Condominium Trust (the “Trust”)

owns, and Longwood Venues & Destinations, Inc.

(“Longwood”) operates, a resort in Harwich Port,

Massachusetts known as the Wychmere Beach Club.

The Beach Club is served by a wastewater treatment

facility that operates under an Individual Groundwater

Discharge Permit issued by the Massachusetts Department of Environmental Protection (“DEP”).

In 2018, amici and other parties were sued in the

United States District Court for the District of

Massachusetts by the Conservation Law Foundation

(“CLF”). Conservation Law Found. v. Longwood Venues

& Destinations, Inc. et al., No. 1:18-cv-11821-WGY

(D. Mass. filed Aug. 24, 2018).2 CLF’s “citizen suit” alleges

that amici and their co-defendants are violating the

Clean Water Act (“CWA”) because (i) while they possess

and operate under a permit from the state, they lack a

federal National Pollutant Discharge Elimination

System (“NPDES”) permit; (ii) one or more elements of

the wastewater treatment facility and its appurtenances is a “point source;” (iii) treated effluent from

the facility contains “pollutants” within the meaning

of the CWA; (iv) some of the treated effluent reaches

local groundwater after being diffused through the

wastewater treatment facility’s leach pits, surrounding

1

Counsel for all parties have consented in writing to the filing

of this brief. Pursuant to Rule 37.6, no counsel for any party

authored this brief in whole or part, and no counsel or party made

a monetary contribution to fund the preparation or submission

of this brief. No person other than amici and their counsel made

any monetary contribution to the preparation or submission of

this brief.

2

The other defendants are affiliated persons and entities, e.g.,

the trustees of the Trust.

2

crushed stone, and soil, as authorized by the state

permit, and (v) some of the allegedly affected groundwater eventually reaches Wychmere Harbor, which is

a “water of the United States.” Am. Compl. for Decl. &

Inj. Relief & Civil Penalties ¶¶ 1–9, Conservation Law

Found. v. Longwood Venues & Destinations, Inc. et al.,

No. 1:18-cv-11821-WGY (D. Mass. filed March 12,

2019), ECF No. 34 (“Amended Complaint”).

The complaint against amici tacitly admits that the

groundwater itself is not a water of the United States.

It alleges, rather, that the CWA applies to the wastewater treatment facility, and that amici therefore

need a federal NPDES permit, only because the local

groundwater is “hydrologically connected” to Wychmere

Harbor, and the groundwater thus is a “conduit”

between the alleged point source and a water of the

United States. Id. ¶¶ 5, 40.

The claims against amici depend on the viability of

the legal theory asserted by the Respondents in this

case, and adopted by the Ninth Circuit in the decision

under review. This Court’s decision, therefore, will

likely be completely dispositive of the case against

amici. Even if it is not conclusive, it will provide

important guidance to the trial court and, if necessary,

to the First Circuit.

SUMMARY OF ARGUMENT

I. Amici’s experiences as the owner and operator

of a state-permitted wastewater treatment facility,

and as the defendants to a citizen suit based on the

hydrologic-connection theory, are representative of

both the success of state regulation and the consequences of the application of the hydrologic-connection

theory.

3

II.A. The hydrologic-connection theory is inconsistent with the Clean Water Act, which memorializes

Congress’s intent to leave regulation of groundwater

to the states.

II.B. Adopting the hydrologic-connection theory

will trigger a broad expansion of the federal NPDES

program with the potential to ensnare millions of

wastewater disposal and treatment systems, simply

because such systems may have contact with local

groundwater, and the groundwater may be “hydrologically connected” to Waters of the United States.

II.C. The owners and operators of many wastewater

disposal and treatment systems will therefore be compelled either (i) to spend significant sums on testing to

determine whether their systems are hydrologically

connected to navigable waters and therefore covered

by the NPDES program, (ii) to spend significant sums

making “blind” and possibly-superfluous NPDES applications, or (iii) to expose themselves to the risk of

financially-crippling citizen suits (like the one currently pending against amici), which can be brought

without governmental oversight and which may be

brought for environmentally-unproductive or improper

reasons.

III. Expansion of the NPDES program is unnecessary, moreover, because rejecting the hydrologicconnection theory will not open a regulatory loophole,

as some courts fear. Amici’s experience demonstrates

that the remedial purposes of the Clean Water Act

can be effectuated without giving short shrift to the

“cooperative federalism” that is an organizing principle of the statute.

4

ARGUMENT

I. Amici’s Circumstances Illustrate The Extent

To Which The Hydrologic-Connection

Theory Will Expand The Scope Of The

NPDES Program.

The Wychmere Beach Club. In the scheme of

things, the Wychmere Beach Club is not a big business. It occupies twenty acres on Cape Cod and

operates for the most part during a season that runs

from April through November. The Beach Club hosts

about 140 private events (such as weddings and

corporate retreats) each year, and offers club amenities (e.g., swimming pools, fitness center, dining room,

childrens’ camp) to approximately 245 members. The

Beach Club also has eighteen guest rooms, which are

available only to members and event guests, and an

equivalent number of employee rooms. Neither the

guest rooms nor the employee rooms are occupied out

of season. Also on the property are residential condominiums.3 Except for the individual condominium

units, the Trust owns the property, which it purchased

in 2010, and Longwood has both managed the condominium and operated the event venue and the club

since then.

The Wastewater Treatment Facility. The Trust

also owns the on-site wastewater treatment facility

that serves the Beach Club. Longwood manages the

facility, primarily by contract with a local environmental engineering firm called Bennett Environmental

Associates, Inc. (“BEA”). BEA specializes in the operation and maintenance of wastewater treatment systems

3

For purposes of brevity, the term “Beach Club,” as used in

this brief, refers collectively to the event venue, the club, and the

residences.

5

and plants, and employs state-licensed wastewater

treatment operators for that purpose.

Wastewater generated by the Beach Club goes first

to one of three 22,000-gallon anoxic tanks for denitrification and the removal of solids. The effluent from

these three tanks is commingled in one 36,000-gallon

equalization tank, and from there it moves through

several additional stages of treatment:

• Placement in rotating biological contactors for

reduction of Biological Oxygen Demand (the

amount of oxygen needed to break down organic

material in the effluent) and the nitrification of

ammonia;

• Conveyance to a weir in which, as needed (including during low flow conditions), a chemical feed

adds carbon to sustain microbial growth and

treatment efficiency, improving denitrification;

• Recirculation to one of the anoxic tanks for

additional treatment as described above, or to

one of two secondary clarifiers for additional

solids removal;

• Conveyance to one of two tertiary dual media

filters, which can remove even very small

suspended solids; and finally,

• Placement in one of twenty-two concrete leaching pits, each one surrounded by crushed stone

in soil four inches above the highest groundwater elevation.4

4

Defs.’ Answer & Affirmative Defenses to Pl.’s Am. Compl.

¶ 46, Conservation Law Found. v. Longwood Venues & Destinations,

Inc. et al., No. 1:18-cv-11821-WGY (D. Mass. Apr. 5, 2019), ECF

No. 49.

6

The volume of wastewater handled, and of effluent

generated, by the wastewater treatment facility is

relatively small. The facility has the capacity to handle

a wastewater flow of up to 80,000 gallons per day

(“gpd”) but it generally operates well below that limit:

for example, in August 2018, at the height of the Beach

Club’s most recent summer season, the average wastewater flow was only 6,991 gpd. Cf. Hawai’i Wildlife

Fund v. Cty. of Maui, 886 F.3d 737, 742 (9th Cir. 2018)

(noting that Lahaina Wastewater Reclamation Facility

receives approximately 4 million gpd of sewage and

injects as much as 2.8 million gpd of effluent into

groundwater via its wells).

The Lack of a NPDES Permit. The wastewater

treatment facility at the Beach Club has an Individual Groundwater Discharge Permit issued by the

Massachusetts DEP. Neither amici nor their predecessors have ever sought or received a NPDES permit.

They have operated the facility solely under the

Massachusetts regulatory regime because they understood, and continue to understand, that state regulation

is both necessary and sufficient. This impression has

recently been confirmed to them at least three times,

in three different ways, by state and federal regulators.

First, in a report submitted to EPA in February

2016 on the Total Maximum Daily Load for Total

Nitrogen in Wychmere Harbor (“the TMDL Report”),

the Massachusetts DEP described the wastewater

treatment facility at the Beach Club as a “non-point

source.”5 Non-point sources are not covered by the

NPDES program. When it approved the Commonwealth’s TMDL Report, moreover, EPA agreed with

DEP’s characterization, referencing the “groundwater

5

Mass. Dep’t of Env. Prot., Total Maximum Daily Load for

Total Nitrogen in Wychmere Harbor (Feb. 2016).

7

discharge of wastewater treatment plant effluent” as

a non-point source.6

Second, in the Interpretive Statement it issued last

month on the application of the NPDES program to

releases of pollutants from a point source to groundwater, EPA surveyed the history of the program with

respect to mechanisms such as septic systems and

wastewater treatment facilities, and noted that “[t]o

date, neither EPA nor states have generally required

NPDES permits for these types of activities, and in

the select instances where NPDES permits have

been required for discharges from a point source that

reaches jurisdictional surface waters via groundwater, they have been based on site-specific factors.”

Interpretive Statement on Application of the Clean

Water Act National Pollutant Discharge Elimination

System Program to Releases of Pollutants from a Point

Source to Groundwater, 84 Fed. Reg. 16,810, 16,812

(Apr. 23, 2019).

Finally, in response to a document subpoena issued

by amici and their co-defendants in the case against

them in the District of Massachusetts, EPA recently

affirmed that it has no records reflecting applications

for NPDES permits for septic systems or other systems

that discharge effluent to the ground or groundwater

in the Commonwealth of Massachusetts from January

1, 2009 to the present, and thus has no records

reflecting agency action on such applications, either.7

6

Mem. in Supp. of Defs.’ Mot. to Dismiss, Exs. A & B, Conservation Law Found. v. Longwood Venues & Destinations, Inc.

et al., No. 1:18-cv-11821-WGY (D. Mass. Nov. 30, 2018), ECF

No. 16.

7

If any such records existed, EPA would have them, because

Massachusetts, unlike most other states, does not administer the

8

The Lawsuit Against Amici. In October 2018,

CLF served amici and several co-defendants with a

complaint that asserted a “citizen suit” under the

CWA. The complaint, as since amended, alleges in

effect that possession of a state permit and compliance

with state regulation is not sufficient in these circumstances, and that the defendants have for years

violated (and are continuing to violate) the CWA by

operating the wastewater treatment facility without a

NPDES permit.8

The Amended Complaint seeks declaratory and

injunctive relief and also, pursuant to the statute, asks

the Court to award CLF both (i) its costs, including

investigative, attorney, witness, and consultant fees,

and (ii) penalties that range from $37,500 per day to

53,484 per day, depending on the date of the alleged

violation, over a period of more than ten years.9

This makes the case a potentially expensive proposition, but what makes it a currently expensive one is

the cost of litigating it under a schedule, set by the

District Court, that puts it on the trial list for

September 2019.10 CLF’s fact discovery, in addition to

the usual interrogatories and requests for admissions

and documents, has included a Federal Rule of Civil

Procedure 34 request for access to the Beach Club

property to perform several days of investigation,

NPDES program by delegation from the federal agency. Upper

Blackstone Water Pollution Abatement Dist. v. EPA, 690 F.3d 9,

14 (1st Cir. 2012).

8

See generally Amended Complaint.

9

Id. ¶ 140.

10

Case Management Order, Conservation Law Found. v.

Longwood Venues & Destinations, Inc. et al., No. 1:18-cv-11821WGY (D. Mass. Feb. 3, 2019), ECF No. 30.

9

including (i) inspection of the wastewater treatment

facility, (ii) inspection of monitoring wells, (iii)

collection of treated sewage samples, (iv) water level

measurements and collection of groundwater samples

from existing wells, (v) construction of new boreholes

and groundwater sampling from them, (vi) observation of lithology, and (vii) water level measurement in

the new boreholes. CLF has hired a consultant to

perform this work, at its own initial expense, but if the

hydrologic-connection theory prevails and CLF wins the

lawsuit it will presumably seek reimbursement as

part of its “investigative . . . and consulting fees.”

II. Adopting

The

Hydrologic-Connection

Theory Will Trigger A Broad Expansion

Of The NPDES Program And Threaten

The Interests Of Millions Of Parties Who

Have Historically Been Regulated By The

States.

The hydrologic-connection theory is a blunt instrument, to say the least. As the Ninth Circuit has

articulated it, the theory requires only a point source,

a discharge to groundwater, and a “fairly traceable”

hydrologic connection between the groundwater and a

water of the United States. Hawai’i Wildlife Fund, 886

F.3d at 749.11 In the matter before the Court, the

hydrologic-connection theory has been applied to a

public wastewater treatment facility (2.8 million gpd),

id. at 742, but the lawsuit against amici evidences the

11

Other versions of the hydrologic-connection theory are

equally broad. For example, according to the Fourth Circuit, the

CWA applies whenever there is a point source, a discharge to

groundwater, and a “direct hydrological connection between

ground water and navigable waters.” Upstate Forever v. Kinder

Morgan Energy Partners, L.P., 887 F.3d 637, 651 (4th Cir. 2018).

10

attempted application of the theory to a much smaller,

privately-owned facility (a maximum of 80,000 gpd),12

and nothing about the theory prevents or discourages

its application to even smaller and less sophisticated

on-site mechanisms, such as a septic system serving a

single household.

Adoption of the hydrologic-connection theory would

therefore presage a dramatic expansion of the scope of

the NPDES program. On Cape Cod, for example, there

are currently more than 123,000 on-site wastewater

systems, serving more than 80% of local businesses

and residences.13 Given the local geography and topography, one cannot rule out the possibility that a “fairly

traceable” or “direct” hydrologic groundwater connection exists between each of those systems and the

Waters of the United States that surround the Cape.

The nationwide percentage is lower—about 18% of

American homes had septic systems in 2017—but that

translates into more than 22 million systems that

discharge effluent to soil and then, potentially, to

groundwater.14

Because population tends to cluster near large

bodies of water, many of those millions of septic systems may “be sufficiently connected to navigable

waters,” Upstate Forever, 887 F.3d at 651, to displace

state regulation and to expose their owners to direct

federal regulation and liability under the CWA. For

example, in 2010 some 123.3 million people, or 39% of

12

Amended Complaint ¶ 60.

13

Cape Cod Commission, Wastewater, http://www.capecod

commission.org/index.php?id=170 (last visited May 10, 2019).

14

U.S. Dep’t of Hous. & Urban Dev. & U.S. Census Bureau,

American Housing Survey for the United States: 2011, at 14

(2013).

11

the nation’s population, lived in Coastal Shoreline

Counties that are directly adjacent to the open ocean,

major estuaries, and the Great Lakes, and 163.8

million people, or 52% of the population, lived in

Coastal Watershed Counties, a designation that

includes land areas within which a significant amount

of water drains into the ocean or Great Lakes.15

Congress never intended to give the NPDES program such a broad scope. Rather, as the Fifth Circuit

discovered when it reviewed the legislative history in

Exxon Corp. v. Train, 554 F.2d 1310 (5th Cir. 1977),

the CWA embodies Congress’s unqualified intention

not “to interfere with or displace the ‘complex and

varied’ state jurisdictions over groundwaters,” id. at

1326; see also id. at 1331, but “to leave the establishment of standards and controls for groundwater pollution to the states . . . .” Id. at 1325. Congress, in other

words, made the deliberate choice to draw a single,

bright line between (i) discharges of pollutants into

navigable waters (subject to regulation under the

NPDES program), and (ii) discharges of pollutants

into groundwater (subject to state regulation).

Nothing in the CWA authorizes the courts to draw

yet another line between sub-classes of discharges in

the second category—e.g., between discharges into

groundwater that has and does not have a sufficient

(whatever that means) “hydrologic connection” to navigable waters. By adopting the hydrologic-connection

theory, then, the Ninth Circuit thwarted Congressional

intent and exceeded its legislative mandate.

15

NOAA, National Coastal Population Report: Population

Trends from 1970 to 2020, at 3–4 (Mar. 2013). These figures, moreover, do not include the millions of Americans who may live and work

far from the coasts but near to other Waters of the United States.

12

Just as important, if this Court adopts the

hydrologic-connection theory, it will imperil large

numbers of home and business owners across the

nation unless and until either Congress acts or the

judiciary engages in still more (and more detailed)

line-drawing exercises. But Congress has shown no

such inclination, and the courts may not find the task

easy to accomplish when acting, as courts must, on a

case-by-case basis. For example, in the decision

under review, the Ninth Circuit suggested that the

hydrologic-connection theory could be limited to

situations in which “the pollutant levels reaching

navigable waters are more than de minimis.” Hawai’i

Wildlife Fund, 886 F.3d at 748. As the Petitioner

points out in its brief, however, this restriction cannot

be squared with the statutory prohibition against

“any addition of any pollutant to navigable waters….”

33 U.S.C. § 1362(12) (2010) (emphasis added).

The Ninth Circuit’s inability to fashion a textuallyconsistent de minimis limitation illustrates how

difficult it may be for the courts to draw the kinds of

boundaries that would be needed to rein in the

hydrologic-connection theory. Until such limits are

set, however, the controlling version of the theory will

implicate parties like amici and millions of residential

septic-system owners, and thus will have pervasive

adverse effects. Many, if not most, on-site wastewater

systems employ soil absorption methods in which

treatment and disposal relies on gradual seepage from

leach fields or leach pits into surrounding soils.16

Even under the best of circumstances, such systems

16

U.S. Env. Prot. Agency, Decentralized Systems Technology

Fact Sheet: Septic Tank Soil Absorption Systems, EPA (Sept.

1999), https://www.h-gac.com/community/water/ossf/DSTFS_Sep

tic-Tank_Soil-Absorption-Systems.pdf.

13

include a “planned release” of effluent from the soil

into the groundwater.17 As long as these systems are

within shouting distance of an ocean, a bay, a river, or

even a wetland, they may have a hydrologic connection

to waters of the United States, and (if the theory holds

sway) they may therefore require a federal NPDES

permit.

Then again, they may not. In every case, the answer

to that question will be literally hidden underground.

The groundwater-that-runs-beneath-the-soil-that-liesbeneath-the-leach-field serving one home or business

may be connected to navigable water while—depending

on local hydrology—the groundwater under a

neighboring leach field may not. Consequently, even if

the Court could draw a clear distinction between the

degrees of hydrologic connections that will and will not

bring the NPDES program into play, the only way to

determine which side of the line any particular home

or business falls on would be to dig—or more precisely,

to engage experts to dig, and then to test, and then to

interpret the results. Governments and large businesses might be able to bear this expense, but it will

be an onerous if not a back-breaking burden for many

homeowners and small businesses, and the effort and

expense will be entirely wasted whenever the answer

turns out to be negative.

Millions of potentially-regulated parties will have

little choice but to shoulder this arbitrary burden,

however, because the alternatives to prophylactic testing and analysis are unpalatable. A business or

home owner could forego testing and file a “blind”

17

Id.

14

application for a NPDES permit, but the administrative process itself would be expensive for the

individual applicant and the collective burden on the

administering agencies would be even greater. To be

sure, a potentially-regulated party could forego both

testing and a NPDES application, and elect to await

instruction from the agencies before taking any action,

but it could do so only by exposing itself to the risk

that, before the government provides its guidance,

somebody will come along and file a citizen suit

requiring expensive litigation and—in the event of an

adverse outcome—statutory penalties.

None of this is required, or in amici’s opinion even

suggested, by the text of the CWA, and nothing in the

Ninth Circuit’s decision explains how such a regime is

supposed to be administered effectively or coherently,

in a way that would actually serve the remedial purposes of the statute, while at the same time respecting

the explicit legislative goal of avoiding undue federal

interference in areas of historic state regulation. 33

U.S.C. § 1251(b) (2011). It is no answer to say that, if

the Court simply enshrines the hydrologic-connection

theory in law, EPA can work out the details.

Redefining the limits of federal jurisdiction, and then

standing up and building out an administrative edifice

to implement a vast expansion of the NPDES program,

would be a herculean task, and even if EPA is given

the resources and capacity to do so eventually, the job

would take years.

In the meantime, it would fall to the judiciary

to adjudicate the cases brought to it. Those cases

will overwhelmingly (if not exclusively) be citizen

suits. Consequently, the exercise of “prosecutorial”

discretion for the newly-expanded NPDES program

would not be democratized so much as it would be

15

anarchized. Anybody who can satisfy the standing

requirements could invoke the hydrologic-connection

theory on the basis of virtually any motive—

impatience with the rate of regulatory progress,

dissatisfaction with the substance of regulatory

oversight, personal animus, or greed. Thus, millions of

business and home owners will be exposed to nuisance

claims, outright shakedowns, and misplaced lawsuits

that serve no real environmental purpose (because, for

example, they target a deep-pocketed defendant that

actually treats its wastewater and therefore makes

only a small contribution to the pollution of navigable

waters, while ignoring other, less affluent or riskaverse polluters whose contribution is much larger).

As long as the selection of cases depends on the

whims and predilections of private plaintiffs, moreover, the resulting patchwork of decisional law may

contain gaps and loopholes that will generate constant

jurisdictional conflicts between the NPDES program

and the “complex and varied” systems of state regulation. Even when those conflicts can be resolved, it will

create a “senseless bifurcation” of state and federal

jurisdiction on the basis of circumstances that Congress

never even considered. Train, 554 F.2d at 1330–31.

III. Rejecting The Hydrologic-Connection

Theory Is Consistent With The Express

Purpose Of The CWA, And Will Not (As

Some Have Claimed) Create A “Loophole”

Allowing The Unregulated Pollution Of

Navigable Waters.

The Ninth and Fourth Circuits have taken the position that rejecting the hydrologic-connection theory

would “make a mockery of the CWA’s prohibitions,”

Hawai’i Wildlife Fund, 886 F.3d at 752, and “greatly

undermine the [remedial] purpose of the Act,” Upstate

16

Forever, 887 F.3d at 652, because “if the presence of a

short distance of soil and ground water were enough

to defeat a claim, polluters could easily avoid liability

under the CWA by ensuring that all discharges pass

through soil and ground water before reaching navigable waters.” Id; see also Tenn. Clean Water Network

v. Tenn. Valley Auth., 905 F.3d 436, 449 (6th Cir. 2018)

(Clay, J., dissenting) (rejecting hydrologic-connection

theory would open a “gaping regulatory loophole”).

This “loophole” rationale has no basis in law or fact.

It is erroneous in the first instance because it misreads

the CWA, focusing on the statute’s remedial purposes

to the unwarranted exclusion of Congress’s express

intention to “recognize, preserve, and protect the primary responsibilities and rights of States to prevent,

reduce, and eliminate pollution [and] to plan the development and use . . . of land and water resources.” 33

U.S.C. § 1251(b). The principle of “cooperative

federalism” that the CWA codified, Kentucky Waterways

All. v. Kentucky Utils. Co., 905 F.3d 925, 929 (6th Cir.

2018), becomes especially important where the type

of regulation at issue “depends on land use controls,

which are traditionally state or local in nature.” Oregon

Natural Desert Ass’n v. United States Forest Serv., 550

F.3d 778, 785 (9th Cir. 2008) (quoting Marc R. Poirier,

Non-point Source Pollution, in Env. Practice Guide

§ 18.13 (2008)).

Cooperative federalism is what impelled Congress to

eschew direct federal regulation of groundwater pollution in the first place, leaving that task to the “complex

and varied” regulatory structures that the states and

their municipalities had already erected and would

continue to maintain. Train, 554 F.2d at 1331 (quoting

S. Rep. No. 414, 92d Cong., 1st Sess. 73 (1971),

reprinted in 1972 U.S. Code Cong. & Admin. News

17

3739). The hydrologic-connection theory thus inserts

the federal NPDES program into what Congress has

clearly marked as state and local territory, and

nothing in the Ninth Circuit’s opinion—or in the opinions of the judges who have worried that respecting

the statutory boundary will create a “loophole” for

those they consider polluters—demonstrates a basis

for overriding Congress’s clearly-expressed intent.

That would be true even if one assumes that

Congress misjudged the states’ willingness and ability

to effectively regulate the groundwater within their

respective jurisdictions: where Congress has drawn a

line, the courts will not cross it. If the courts espousing

the “loophole” rationale made that unspoken assumption, moreover, they assumed facts not in evidence. As

far as amici are aware, nobody has yet suggested,

much less shown at any relevant level of generality,

that federal regulation will be more effective than

the existing framework of state regulatory regimes.

Adopting the hydrologic-connection theory would—for

amici and many similarly-situated parties—undeniably add a new level of expense and administrative

burden (not to mention the potential for crippling

penalties), but its impact on the environment, beneficial or otherwise, is purely a matter of speculation.

Amici believe that their experience in Massachusetts

demonstrates that the concerns underlying the

“loophole” rationale are in fact illusory. For one thing,

giving the Commonwealth primary responsibility for

the regulation of its groundwater, as Congress envisioned, has not excluded the federal government from

the process. Like Hawaii and every other state,

Massachusetts regulates its groundwater under the

federal statute, which gives the federal government a

meaningful, albeit indirect, role. In compliance with

18

the CWA, for example, the Massachusetts DEP has

issued, and EPA has approved, a Nonpoint Source

Management Program Plan for the Commonwealth.18

Among other things, the Massachusetts Plan designates

Cape Cod as a region that requires the development

and implementation of an area-wide waste management plan.19 In 2013, the Cape Cod Commission was

assigned that task and instructed specifically to

address nutrient pollution of the sort alleged in the

lawsuit against amici. Id. The Commission has been

actively carrying out this mandate, producing a

Regional Wastewater Management Plan that EPA will

also review and approve upon its completion. Id.20

The Commonwealth of Massachusetts, for its part,

takes its statutory responsibility seriously and does its

job well. The safe and environmentally sound operation of privately-owned, on-site septic systems and

wastewater treatment facilities is clearly a matter

of considerable importance to the Commonwealth,

which regulates these mechanisms as part of a robust

and comprehensive regime for the protection of its

groundwater. Wastewater treatment facilities like the

one that amici own and operate are subject to the

Commonwealth’s Ground Water Discharge Permit

Program. 314 Mass. Code Regs. 5.00 et seq. (2016),

Massachusetts Clean Waters Act, Mass. Gen. Laws ch.

21, § 26; see also 314 Mass Code Regs. 5.03, 5.05(1)(a)

(2016) (requiring a DEP permit for discharges of

18

See generally Mass. Dep’t of Env. Prot., Massachusetts

Nonpoint Source Management Program Plan 2014–2019 (2014).

19

20

Id. at 42.

See also Cape Cod Commission, Regional Wastewater

Management Plan, Cape Cod Commission (last visited May 13,

2019), http://www.capecod commission.org/regionalplans/RWMP

(last visited May 13, 2019).

19

pollutants to ground waters of the Commonwealth

except from a facility that discharges treated effluent

and is designed to receive and receives less than

10,000 gpd).21

The Ground Water Discharge Permit Program is

designed, among other things, to ensure that discharges

which reach groundwater do not subsequently cause or

contribute to violations of the Commonwealth’s regulatory standards for surface water quality. 314 Mass.

Code Regs. 4.00 et seq. (2013). The Massachusetts

Surface Water Quality Standards are in turn designed

“to secure to the Commonwealth the benefits of the

Clean Water Act, 33 U.S.C. § 1251 et seq.” 314 Mass.

Code Regs. 4.01(4) (2013) (describing the “Purpose” of

the Massachusetts Surface Water Quality Standards).

In order to achieve this goal, every Individual

Groundwater Discharge Permit the Massachusetts

DEP issues must “contain limits which are adequate

to protect surface waters for their existing and

designated uses and to assure the attainment and

maintenance of [the Massachusetts Surface Water

Quality Standards].” 314 Mass. Code Regs. 5.10(3)

(2016). In particular, the permit limitations must

“protect existing uses of hydrologically connected

downgradient ground waters and surface waters, and

shall not interfere with the maintenance and attainment of beneficial uses in hydrologically connected

downgradient waters.” Id.

21

Smaller treatment facilities and septic systems are covered

separately by the regulatory program commonly known as

“Title V.” 310 Mass. Code Regs. 15.000 et seq. (2016) (“Standard

Requirements for the Siting, Construction, Inspection, Upgrade

and Expansion of On-Site Sewage Treatment and Disposal

Systems and for the Transport and Disposal of Septage”).

20

Massachusetts, in other words, has a system in

place that not only regulates discharges of effluent

from wastewater treatment facilities, and not only

regulates such discharges for the purpose of protecting

groundwater that may come into contact with the

treated effluent, but also regulates such discharges

for the broader purpose of protecting surface waters,

including surface waters that may be affected because

they are “hydrologically connected” to the local

groundwater.

Amici’s wastewater treatment facility operates

within that system, under the terms of an Individual

Groundwater Discharge Permit that was most

recently renewed in November 2018. The Permit’s

General Conditions require compliance with various

statutory and regulatory provisions, but the Permit

also contains Special Conditions that include facilityspecific discharge limitations on various effluent

characteristics: flow, oil and grease, Total Suspended

Solids, Total Nitrogen, Nitrate-Nitrogen, Biochemical

Oxygen Demand, and pH value. The Special Conditions

also require periodic testing of both influent and

effluent at the facility, as well as regular analysis of

groundwater samples drawn from four permanent

monitoring wells located on the property.

The Commonwealth’s regulatory structure, in sum,

is reality-tested, consistent with cooperative federalism

and, perhaps most important, free of the administrative burdens and wasted expenditures that would

follow from the adoption of the hydrologic-connection

theory—a theory that permits federal regulation of

some groundwater, but not other groundwater, and

that requires this essential distinction to be made on

the basis of a latent characteristic that must be uncovered before it can effectively be discerned. Massachusetts

21

already regulates all of the groundwater in its jurisdiction, eliminating the need for such “senseless

bifurcations,” and since the Commonwealth regulates

its groundwater for, among other things, the express

purpose of protecting surface waters and securing the

benefits of the Clean Water Act, it does so in a way

that effectively promotes both the remedial and the

cooperatively-federalist goals of that statute.

CONCLUSION

Amici respectfully ask the Court to reverse the

judgment below.

Respectfully submitted,

KEVIN M. MCGINTY

Counsel of Record

JEFFREY R. PORTER

ANDREW NATHANSON

EMILY KANSTROOM MUSGRAVE

MINTZ, LEVIN, COHN, FERRIS,

GLOVSKY AND POPEO, P.C.

One Financial Center

Boston, MA 02111

(617) 542-6000

kmcginty@mintz.com

Counsel for Amici Curiae

May 16, 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.

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Amicus Curiae Brief — County of Maui, Hawaii, Petitioner v. Hawaii Wildlife Fund, et al. | Frix