Document ID: s3://data.kl3m.ai/documents/govinfo/USCOURTS/USCOURTS-ca11-15-14745/USCOURTS-ca11-15-14745-0/pdf.json

Parties Involved:
Alabama Coal Association
Appellee
Black Warrior Riverkeeper, Inc.
Appellant
Thomas P. Bostick
Appellee
Jon Chytka
Appellee
Defenders of Wildlife
Appellant
MS & R Equipment Co., Inc.
Appellee
Reed Minerals, Inc.
Appellee
Twin Pines, LLC
Appellee
U.S. Army Corps of Engineers
Appellee
Walter Minerals, Inc.
Appellee

Document Text:

[PUBLISH]

IN THE UNITED STATES COURT OF APPEALS

FOR THE ELEVENTH CIRCUIT

________________________

No. 15-14745

________________________

D.C. Docket No. 2:13-cv-02136-WMA

BLACK WARRIOR RIVERKEEPER, INC.,

DEFENDERS OF WILDLIFE, 

 Plaintiffs - Appellants, 

versus

U.S ARMY CORPS OF ENGINEERS, 

LT GENERAL THOMAS P. BOSTICK, 

U.S. Army Corps of Engineers, 

COL. JON CHYTKA, 

U.S. Army Corps of Engineers, Mobile District, 

 Defendants - Appellees.

________________________

Appeal from the United States District Court

for the Northern District of Alabama

________________________

(August 12, 2016)

Before TJOFLAT and MARCUS, Circuit Judges, and STEELE,* District Judge.

 * Honorable John E. Steele, United States District Judge for the Middle District of 

Florida, sitting by designation.

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MARCUS, Circuit Judge:

In this appeal, we consider -- for the second time -- whether the United 

States Army Corps of Engineers’ (“Corps”) 2012 decision to reissue Nationwide 

Permit 21 (“NWP 21”), a general permit regulating discharge of dredged or fill 

materials into navigable waters by surface coal mining operations, was arbitrary

and capricious. Under Section 404 of the Clean Water Act (“CWA”), the Corps

may authorize the discharge of fill materials into navigable waters of the United 

States by issuing a “general permit” only if those activities will result in minimal 

individual and cumulative adverse effect on the aquatic environment. See 33 

U.S.C. § 1344(e)(1). And the National Environmental Policy Act (“NEPA”) 

requires that federal agencies evaluate whether their proposed actions are likely to 

have a significant impact on the environment. See 42 U.S.C. § 4332. The 2012 

NWP 21 imposes strict discharge limits on all new surface mining activities, but 

grandfathers in activities approved under a previous iteration of NWP 21 so long as 

they do not exceed previously approved discharge levels and meet other conditions 

imposed by a regional Corps official. At the headwaters of this litigation, Black 

Warrior Riverkeeper, Inc., and Defenders of Wildlife (collectively “Riverkeeper”), 

two concerned environmental groups, filed suit under the Administrative 

Procedure Act, 5 U.S.C. § 706, claiming that the Corps’ decision to reissue NWP 

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21, as well as its environmental impact findings under the CWA and NEPA, were 

arbitrary and capricious.

The first time around, the district court granted summary judgment to the 

Corps and Riverkeeper appealed. However, on the eve of oral argument, the Corps 

admitted that it had failed to consider certain important information in reaching its 

decision, so we remanded the case to the district court, which in turn remanded it 

to the Corps for further review. After considering the omitted data, the Corps 

reaffirmed its decision to issue NWP 21. Riverkeeper renewed its challenges, and

the district court once again granted final summary judgment in favor of the Corps. 

Riverkeeper again appeals, arguing that the Corps’ decision to treat new and old 

activities differently can’t hold water. After thorough review and with the benefit 

of oral argument, we affirm.

I.

A.

As we explained the first time we heard this case, see Black Warrior 

Riverkeeper, Inc. v. U.S. Army Corps of Eng’rs., 781 F.3d 1271, 1275–78 (11th 

Cir. 2015), Riverkeeper’s challenge involves several complex statutory and 

regulatory schemes designed, in substantial measure, to ensure that federal 

agencies conduct a thorough assessment of the environmental impacts of their 

proposed actions. The Clean Water Act prohibits the “discharge of any pollutant”

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into “navigable waters” unless in compliance with specified provisions of the Act. 

33 U.S.C. §§ 1311(a), 1344(a); see also U.S. Army Corps of Eng’rs. v. Hawks Co., 

Inc., 136 S. Ct. 1807, 1811 (2016). “Pollutant” includes “rock” and “sand,” 33 

U.S.C. § 1362(6), and “[n]avigable waters” encompass all “waters of the United 

States,” id. § 1362(7). Despite the CWA’s general prohibition on the discharge of 

pollutants, Section 404 of the Act expressly authorizes the Secretary of the Army, 

through the Corps, to regulate discharges of dredged or fill material -- a subset of 

“pollutants” -- into waters of the United States through the issuance of permits. 

See 33 U.S.C. § 1344. These permits can take the form of either individual 

permits, § 1344(a), or general permits, which authorize certain categories of 

discharges on a state, regional, or nationwide basis, § 1344(e). 

The Corps reviews “individual” permit applications on a case-by-case basis 

under Section 404(a). Id. § 1344(a). Individual permits may be issued or denied 

after a review involving, among other things, site-specific documentation and 

analysis, opportunity for public hearing, public interest review, and a formal 

determination that the permit is lawful and warranted. See 33 C.F.R. § 323.3 

(specifying activities requiring permits); 33 C.F.R. pts. 320, 323, 325 (policies and 

procedures for permit processing). Issuing an individual permit “requires a 

resource-intensive review that entails submission of voluminous application 

materials, extensive site-specific research and documentation, promulgation of 

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public notice, opportunity for public comment, consultation with other federal 

agencies, and a formal analysis justifying the ultimate decision to issue or refuse 

the permit.” Crutchfield v. County of Hanover, 325 F.3d 211, 214 (4th Cir. 2003).

To avoid the burden of individual permit evaluations, Congress authorized 

the Corps to issue general permits to cover categories of discharges that, as a 

group, have only minimal impacts on the waters of the United States. H.R. Rep. 

No. 95-830, at 98 (1977). General permits may be issued “on a State, regional, or 

nationwide basis for any category of activities involving discharges of dredged or 

fill material” by the Corps’ Chief of Engineers or a District Engineer, which is a 

regional official, but only after an extensive administrative process and analysis at 

the national or regional level. 33 U.S.C. § 1344(e)(1). Before issuing a general 

permit, then, the Corps must provide public notice and an opportunity for a 

hearing. Id. And before it can be issued, the Corps must determine that the 

proposed general permit meets three conditions: the activities authorized by the 

permit must (1) be “similar in nature,” (2) cause only “minimal adverse 

environmental effects when performed separately,” and (3) “have only minimal 

cumulative adverse effect on the environment.” Id. In determining whether the 

environmental effects of a general permit will be minimal, the Corps must consider 

a range of factors relating to the impact of discharges on aquatic ecosystems and 

the humans who use them, and must then document the environmental effects of 

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the activities authorized by the permit in a decision document. See 40 C.F.R. pt. 

230 (2014). 

After performing this evaluation, the Corps must make a written 

determination of the effects of a proposed activity “on the physical, chemical, and 

biological components of the aquatic environment.” 40 C.F.R. § 230.11. The 

decision document must provide specific documentation showing that each of the 

§ 1344(e) conditions has been met, and the evaluation “must be completed before 

any General permit is issued.” See 40 C.F.R. § 230.7(b). 

The Corps is also required to comply with the National Environmental 

Policy Act. NEPA serves the dual purpose of informing agency decisionmakers of 

the environmental effects of proposed federal actions and ensuring that relevant 

information is made available to members of the public so that they “may also play 

a role in both the decisionmaking process and the implementation of that decision.” 

Robertson v. Methow Valley Citizens Council, 490 U.S. 332, 349 (1989). NEPA’s 

mandate to agencies is “essentially procedural . . . . It is to insure a fully informed 

and well-considered decision . . . .” Vt. Yankee Nuclear Power Corp. v. Nat. Res. 

Def. Council, Inc., 435 U.S. 519, 558 (1978). Thus, “it is now well settled that 

NEPA itself does not mandate particular results, but simply prescribes the 

necessary process.” Robertson, 490 U.S. at 350. NEPA requires federal agencies 

to prepare an Environmental Impact Statement for any “major Federal action[] 

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significantly affecting the quality of the human environment,” which can include 

nationwide permits issued by the Corps. 42 U.S.C. § 4332(2)(C); 33 C.F.R. § 

330.5(b)(3). The agency first prepares an Environmental Assessment, which is 

essentially a preliminary account of the environmental effects of a proposed action. 

See 40 C.F.R. §§ 1501.4, 1508.9. If the Environmental Assessment suggests that 

the effects of the action are likely to be significant, the agency must issue the more 

detailed Environmental Impact Statement. See id. § 1501.4(c). Otherwise, it 

issues a Finding of No Significant Impact. Id. § 1501.4(e).

B.

This case involves a challenge to Nationwide Permit 21 (“NWP 21”), a 

general permit issued by the Corps. On February 21, 2012, after affording the 

public the opportunity to participate in an administrative process that included 

notice and comment, the Corps issued fifty nationwide permits, including NWP 21. 

Reissuance of Nationwide Permits, 77 Fed. Reg. 10,184 (Feb. 21, 2012). NWP 21 

authorizes “[d]ischarges of dredged or fill material into waters of the United States 

associated with surface coal mining and reclamation operations.” Id. at 10,274. 

Surface coal mining involves the discharge of dredged or fill material in a 

variety of ways. To reach underground coal seams, surface mining operations 

must dig through and remove a mixture of soil, rock, and coal residue commonly 

referred to as “overburden,” which is replaced once the coal has been extracted. 

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Excess overburden must be deposited somewhere else -- occasionally filling or 

burying streams, or in the form of a much larger “valley fill,” which is exactly 

what it sounds like. In other cases, the coal seam runs underneath the stream itself, 

and the operation will “mine through” the stream. Mining operations also generate 

and discharge material when they create sediment ponds and build roads, 

processing plants, and other mining infrastructure. As a result of the mining 

process, drainage from the mining site, which contains substantial amounts of 

sediment, salt, and metals, can seep into and contaminate larger waterways. This 

runoff may continue for decades after the mine has closed. The discharge of 

dredged or fill material, therefore, may have consequences for water quality and 

the health of aquatic ecosystems throughout the entire watershed.

The Corps has long struggled to ensure that the environmental impacts of 

surface mining operations are minimal. Nationwide Permit 21 was first issued in 

1982, see Interim Final Rule for Regulatory Programs of the Corps of Engineers, 

47 Fed. Reg. 31,794, 31,833 (July 22, 1982), and has subsequently been amended 

and reissued many times. The 2007 version did not place any limits on the length 

of streams that could be filled by authorized activities. See Reissuance of 

Nationwide Permits, 72 Fed. Reg. 11,092, 11,184 (Mar. 12, 2007). The Corps 

eventually became concerned that activities authorized by NWP 21 were resulting 

in greater environmental impacts than anticipated, and it suspended NWP 21 in six 

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states in the Appalachian Region in 2010: Kentucky, Ohio, Pennsylvania, 

Tennessee, Virginia, and West Virginia. See Suspension of Nationwide Permit 21, 

75 Fed. Reg. 34,711, 34,712 (June 18, 2010). The Corps did not suspend NWP 21 

in Alabama, although the Environmental Protection Agency subsequently stated in 

a letter to the Corps that “the same concerns and science that brought about the six 

state suspension appl[y] to the coal fields of Alabama.” The 2007 NWP 21 expired 

on March 18, 2012. Reissuance of Nationwide Permits, 72 Fed. Reg. at 11,092.

In 2012, the Corps adopted a new course intended, in part, to “address[] the 

concern that led to [its] previous suspension of NWP 21 in the six Appalachian 

states.” Reissuance of Nationwide Permits, 77 Fed. Reg. at 10,205. During the 

notice and comment period, the Corps proposed three options for reauthorizing 

NWP 21 after its expiration:

The first option was not to reissue NWP 21 and to let it expire on 

March 18, 2012. . . . Option 2 was to reissue NWP 21 with a 1⁄2-acre 

limit, including a 300 linear foot limit for the loss of stream bed. 

Under Option 2, NWP 21 would not authorizes discharges of . . . 

valley fills. . . . Option 3 was similar to Option 2, but under Option 3 

NWP 21 could authorize discharges of . . . valley fills.

In 2012, the Corps “selected Option 2 for the reissuance of NWP 21, and [] made 

some additional modifications to reduce hardships on permittees who previously 

obtained authorization under the NWP 21 issued on March 12, 2007, and invested 

substantial resources in reliance on that NWP authorization.” 

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As a result, the 2012 version of NWP 21, which authorized stream-filling 

operations for an additional five years, consisted largely of two new provisions.1

 1 The full text of the 2012 NWP 21 provides:

21. Surface Coal Mining Activities. Discharges of dredged or fill material into 

waters of the United States associated with surface coal mining and reclamation 

operations.

(a) Previously Authorized Surface Coal Mining Activities. Surface 

coal mining activities that were previously authorized by the NWP 

21 issued on March 12, 2007 (see 72 FR 11092), are authorized by 

this NWP, provided the following criteria are met:

(1) The activities are already authorized, or are currently 

being processed by states with approved programs under 

Title V of the Surface Mining Control and Reclamation Act 

of 1977 or as part of an integrated permit processing 

procedure by the Department of Interior, Office of Surface 

Mining Reclamation and Enforcement;

(2) The permittee must submit a letter to the district 

engineer requesting re-verification of the NWP 21 

authorization. The letter must describe any changes from 

the previous NWP 21 verification. The letter must be 

submitted to the district engineer by February 1, 2013;

(3) The loss of waters of the United States is not greater 

than the loss of waters of the United States previously 

verified by the district engineer under the NWP 21 issued 

on March 12, 2007 (i.e., there are no proposed expansions 

of surface coal mining activities in waters of the United 

States);

(4) The district engineer provides written verification that 

those activities will result in minimal individual and 

cumulative adverse effects and are authorized by NWP 21, 

including currently applicable regional conditions and any 

activity-specific conditions added to the NWP authorization 

by the district engineer, such as compensatory mitigation 

requirements; and

(5) If the permittee does not receive a written verification 

from the district engineer prior to March 18, 2013, the 

permittee must cease all activities until such verification is 

received. The district engineer may extend the February 1, 

2013, deadline by so notifying the permittee in writing, but 

the permittee must still cease all activities if he or she has 

(continued on next page)

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First, paragraph (a), which functions as a grandfathering provision, allows for the 

reauthorization of operations that were previously authorized under the 2007 NWP 

21, subject to verification by a district engineer that the activity will not impact 

more waters than previously authorized under the 2007 NWP, will continue to 

cause only minimal individual and cumulative adverse effects, and will comply 

 

not received written verification from the Corps by March 

18, 2013, until such verification is received.

(b) Other Surface Coal Mining Activities. Surface coal mining 

activities that were not previously authorized by the NWP 21 

issued on March 12, 2007, are authorized by this NWP, provided 

the following criteria are met:

(1) The activities are already authorized, or are currently 

being processed by states with approved programs under 

Title V of the Surface Mining Control and Reclamation Act 

of 1977 or as part of an integrated permit processing 

procedure by the Department of Interior, Office of Surface 

Mining Reclamation and Enforcement;

(2) The discharge must not cause the loss of greater than 1⁄2-

acre of non-tidal waters of the United States, including the 

loss of no more than 300 linear feet of stream bed, unless

for intermittent and ephemeral stream beds the district 

engineer waives the 300 linear foot limit by making a 

written determination concluding that the discharge will 

result in minimal individual and cumulative adverse effects. 

This NWP does not authorize discharges into tidal waters 

or non-tidal wetlands adjacent to tidal waters; and

(3) The discharge is not associated with the construction of 

valley fills. A “valley fill” is a fill structure that is typically 

constructed within valleys associated with steep, 

mountainous terrain, associated with surface coal mining 

activities.

Notification: For activities under paragraph (b) of this NWP, the permittee must 

submit a pre-construction notification to the district engineer and receive written 

authorization prior to commencing the activity. (See general condition 31.) 

(Sections 10 and 404)

Reissuance of Nationwide Permits, 77 Fed. Reg. at 10,274.

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with any additional activity-specific conditions that the district engineer deems 

appropriate, such as compensatory mitigation.

2 Id. at 10,274. As for new 

operations, paragraph (b) adds several specific limits on stream-filling activity, 

including a requirement that discharges “must not cause the loss of greater than 1⁄2-

acre of non-tidal waters of the United States, including the loss of no more than 

300 linear feet of stream bed.” Id. Permitted activities under 21(b) also may not 

involve the construction of valley fills. Id. The new limits provided by paragraph 

(b) do not apply to grandfathered reauthorizations under paragraph (a) -- and that 

disparate treatment forms the crux of the Riverkeeper’s challenge in this case.

Along with the revised permit, the Corps issued a sixty-four page Decision 

Document explaining the rationale behind its revisions, which included the Corps’

Clean Water Act and National Environmental Policy Act analyses. Specifically, 

the Corps estimated that, in total, NWP 21 would be used approximately 61 times 

per year on a national basis, resulting in impacts to approximately 26 acres of 

waters of the United States, and requiring approximately 62 acres of compensatory 

mitigation to offset the impacts. The Corps concluded, as required by the CWA, 

 2 Compensatory mitigation “involves actions taken to offset unavoidable adverse impacts 

to wetlands, streams and other aquatic resources authorized by Clean Water Act section 404 

permits and other aquatic resources authorized by Clean Water Act section 404 permits.” 

Compensatory Mitigation for Losses of Aquatic Resources, 73 FR 19594-01, 19594 (April 10, 

2008). “Compensatory mitigation can be carried out through four methods: the restoration of a 

previously-existing wetland or other aquatic site, the enhancement of an existing aquatic site’s 

functions, the establishment (i.e., creation) of a new aquatic site, or the preservation of an 

existing aquatic site.” Id. 

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that activities authorized by NWP 21 would not have more than minimal 

cumulative adverse effect on the environment. It also concluded, pursuant to 

NEPA, that NWP 21 would not significantly affect the environment, and that an 

Environmental Impact Statement would therefore not be required. Certain portions 

of the Decision Document suggested that the limitations imposed on new 

authorizations under paragraph 21(b) were “necessary to constrain the adverse 

effects to the aquatic environment, to ensure compliance with the statutory 

requirement that general permits, including NWPs, may only authorize those 

activities that have minimal individual and cumulative adverse effects on the 

aquatic environment.” 

C.

Riverkeeper is an environmentalist group whose members use waters of the 

Black Warrior River watershed, in west-central Alabama, that flow downstream 

from mining sites authorized to discharge material under NWP 21. According to 

Riverkeeper, these projects have had a profound effect on the quality of the waters 

within the Black Warrior River watershed. Its members have observed, for 

example, that waters downstream from mining sites are discolored and clouded 

with sediment and silt. Impaired water quality, they claim, has “decrease[d] [their] 

aesthetic and recreational enjoyment, reduce[d] their opportunities to observe 

wildlife, and cause[d] them concern about ingesting the water and fish caught in 

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the water.” To take just one example, Riverkeeper alleges that several coal mines 

permitted under NWP 21(a) ultimately drain into the Locust Fork of the Black 

Warrior River, near Birmingham, releasing sedimentation, solids, and chemical 

compounds. Riverkeeper fears that what it calls the resulting “dirty or polluted 

water” will deter its members and others from using the river for recreation -- the 

Locust Fork is one of the most popular whitewater paddling locations in the state --

as well as harm local wildlife. 

In order to block the forty-one reauthorizations granted by the Corps 

pursuant to NWP 21(a) and therefore avert further claimed environmental damage, 

Riverkeeper filed this lawsuit in the United States District Court for the Northern 

District of Alabama on November 25, 2013, against the Corps and several Corps 

officials. The gravamen of Riverkeeper’s complaint is that it was contradictory for 

the Corps to impose stringent stream-fill limits on new operations, but, at the same 

time, decline to apply those very same limits to operations previously authorized 

by the 2007 NWP 21 and subsequently reauthorized by the 2012 version. To put it 

slightly differently, Riverkeeper’s argument is that the Corps could not rationally 

have found (as the Decision Document suggested) that these new limits were 

“necessary” to avoid significant environmental impacts, and then conclude 

regardless that the impacts of grandfathered projects would be minimal. 

Specifically, Riverkeeper’s complaint raised four counts: (1) paragraph (a) of NWP 

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21, in effect, amounts to an unlawful ten-year permit term, in violation of 33 

U.S.C. § 1344(e)(2); (2) the Corps’ cumulative effects analysis under the CWA 

was arbitrary and capricious, in violation of 5 U.S.C. § 706 and 33 U.S.C. § 

1344(e)(1); (3) the Corps’ issuance of reauthorizations in the Black Warrior River 

watershed pursuant to NWP 21 was arbitrary and capricious, in violation of 5 

U.S.C. § 706 and 33 U.S.C. § 1344(e)(1); and (4) the Corps’ Finding of No 

Significant Impact under NEPA was arbitrary and capricious, in violation of 5 

U.S.C. § 706 and 42 U.S.C. § 4332(c). 

Eight days after it initiated this suit, Riverkeeper moved for a preliminary 

injunction to suspend all reauthorizations in the Black Warrior River watershed. 

On December 23, 2013, the Alabama Coal Association and several mining 

companies -- MS & R Equipment Co., Inc., Reed Minerals, Inc., Twin Pines, LLC, 

and Walter Minerals, Inc. -- moved to intervene, citing the harm that Riverkeeper’s 

requested injunction would cause to their mining operations. Their motion to 

intervene was granted without objection from Riverkeeper. At a February 2014 

hearing on Riverkeeper’s motion for a preliminary injunction, the district court 

refused to hear any argument on the merits because Riverkeeper could not post a 

$300,000 bond. The district court denied Riverkeeper’s motion on February 18. 

Riverkeeper then moved for summary judgment on February 20. At a hearing on 

March 3, Riverkeeper voluntarily dismissed Count 3 of its complaint, claiming that 

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it was no longer directly challenging the forty-one reauthorizations. On April 2, 

the Corps filed a cross-motion for summary judgment, addressing the merits; a 

week later, the Intervenors filed their motion to dismiss or for summary judgment, 

addressing the merits as well as standing and laches. 

Ultimately, the district court concluded that Riverkeeper had standing under 

Article III of the U.S. Constitution and the Administrative Procedure Act to mount 

this lawsuit, but that its claims were barred by the doctrine of laches, and, in any 

event, failed on the merits. The district court rejected the Intervenors’ argument 

that Riverkeeper lacks standing to challenge a permit under § 404 because 

Riverkeeper’s injuries, which flow from diminished downstream water quality, 

were cognizable under § 404 and traceable to NWP 21. The district court did, 

however, decide that Riverkeeper’s delay in commencing this lawsuit was 

inexcusable, and that the Intervenors suffered palpable prejudice because they 

acted in reliance on reauthorizations granted under NWP 21. Finally, the district 

court concluded that the Corps did not act arbitrarily and capriciously in 

concluding that NWP 21 would have no more than minimal cumulative adverse

effect on the environment. Riverkeeper timely appealed to this Court.

On March 23, 2015, a panel of this Court vacated the district court’s 

decision. See Black Warrior Riverkeeper, 781 F.3d at 1292. It agreed with the 

district court that the plaintiffs had standing to pursue both its Clean Water Act and 

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National Environmental Policy Act claims challenging the reissuance of NWP 21. 

Id. at 1283. But it found that the district court had abused its discretion in finding 

that the plaintiffs’ suit was barred by laches, both because they had shown 

adequate excuse for their delay in filing suit and because their delay did not 

prejudice the defendants or intervenors. Id. at 1284-85, 1287. 

Turning to the merits, the panel explained that Riverkeeper challenged only 

a single error of the Corps’ reasoning, which it called the “differential treatment 

error.” Id. at 1288. In short, Riverkeeper argued that “it was arbitrary and 

capricious for the Corps to conclude, on the one hand, that the new stream-fill 

limits contained in paragraph (b) of NWP 21 are necessary to avoid significant 

environmental effects, but on the other, to decline to apply them to projects 

reauthorized pursuant to paragraph (a).” Id. However, the panel concluded that it 

could not resolve the merits of the suit because “the Corps admitted on the eve of 

oral argument that it underestimated the number of acres of waters that may be 

impacted by NWP 21.” Id. at 1288. Specifically, the Corps had failed to “take 

into account that activities re-verified under paragraph (a)” -- the grandfathered-in

activities that were not subject to the new limitations imposed by paragraph 21(b) -

- “could impact more than a half-acre of waters of the United States.” Id. On this 

murky record, the Court could not discern whether the Corps’ error was “truly 

significant” and whether the Corps’ “ultimate conclusion -- that NWP 21 will have 

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minimal effects -- was unlawful.” Id. The panel declined to vacate NWP 21, 

concluding that vacatur was not mandatory and that it had the equitable discretion 

to remand the matter to the Corps without vacating the agency’s action. Id. at 

1289. However, viewing the undeveloped record, the panel could not decide in 

which direction the equities tipped. Id. at 1291. Therefore, the panel vacated the 

district court’s decision and remanded with instructions to the district court to 

remand the case to the Corps with a one-year time limit to reconsider its decision, 

and to determine whether any further relief, including vacatur, was required in 

light of the Corps’ admitted error. Id.3

D.

The district court sent the case back upstream to the Corps “for a thorough 

reevaluation of the Corps’ CWA and NEPA determinations in light of all of the 

relevant data, including the Corps’ recalculated figure for the acreage of waters 

affected by NWP 21.” It ordered that the reevaluation be accomplished within a 

year and stayed the case pending completion of the reevaluation. But the district 

court declined to vacate NWP 21 pending reevaluation because the reevaluation 

would take less than a year and there was “no indication that intervenors intend to 

 3 U.S. District Judge Totenberg agreed with the Court on standing and laches, but thought 

that the Corps’ confessed error was so significant as to require vacatur of NWP 21. Black 

Warrior Riverkeeper, 781 F.3d at 1292 (Totenberg, J., concurring in part and dissenting in part).

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perform material alterations to the subject water quality while the reconsideration 

is ongoing.”

Six weeks later, on August 7, 2015, the Corps submitted a Revised Decision 

Document to the district court. The Revised Decision Document did not result in 

any changes to NWP 21, but did provide an updated analysis of the impacts of the 

permit. It analyzed the actual impact of paragraph (a), which was the flaw that the 

Corps had confessed to on the eve of oral argument. Because paragraph (a) 

required new verifications of the previously authorized projects to issue before 

March 18, 2013, a date which had long passed by the time the Revised Decision 

Document was drafted, the Corps was able to provide an estimate of environmental 

impact that encompassed all of the NWP 21(a) verifications that could be issued.

In all, 88 verifications were issued under 21(a), with impacts to approximately 503 

acres and 280,700 linear feet of waters of the United States. To offset those 

impacts, the Corps required compensatory mitigation of approximately 653 acres 

and 377,300 linear feet. The Corps determined that 21(b) would be used 

approximately 7 times per year nationwide, resulting (over the life of the permit) in 

impacts to approximately 6.5 acres and 17,000 linear feet of waters of the United 

States, and requiring 11.5 acres and 21,000 linear feet of compensatory mitigation 

to offset the impacts. Thus, on average, each of the 21(a) authorizations impacts 

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nearly 6 acres and 3,200 linear feet of waters of the United States (in comparison 

with the 1⁄2-acre and 300 linear feet limits imposed on all 21(b) authorizations). 

The Revised Decision Document contained essentially the same statements 

on which the Riverkeeper’s “differential treatment error” argument had been 

based. For example, it states that the acreage and linear foot limits in NWP 21(b) 

“are necessary to constrain the adverse effects to the aquatic environment to ensure 

compliance with the statutory requirement that general permits, including NWPs, 

may only authorize those activities that have minimal individual and cumulative 

adverse effects on the aquatic environment.” It also provides that “[t]he new 

acreage and linear foot limits will ensure that this NWP contributes no more than 

minimal individual and cumulative adverse effects to the aquatic environment,”

and that “[t]he Corps has determined that the changes to NWP 21 are necessary to 

comply with the requirements of Section 404(e) of the Clean Water Act.”

The Corps’ overall findings were not affected by its adjustment to the impact 

of 21(a). It concluded, as required by the CWA, that “despite the higher impact 

and compensatory mitigation amounts expected to occur across the country during 

the five year period this NWP is in effect, . . . the individual and cumulative 

adverse effects on the aquatic environment resulting from the activities authorized 

by this NWP will be minimal.” The Corps also made a “Finding of No Significant 

Impact” under NEPA. 

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After reviewing the Revised Decision Document, the parties renewed their 

cross-motions for summary judgment. The district court again granted the Corps’

motion for summary judgment and denied the plaintiffs’ motion for summary 

judgment. It noted that Riverkeeper raised the same “differential treatment error”

argument based on language in the Revised Decision Document that is 

indistinguishably similar to the language it relied on in the original decision 

document. The court rejected that argument because it determined that statements 

in the Revised Decision Document that the changes to NWP 21 were “necessary”

to ensure minimal environmental impact logically referred to all changes and all 

new terms and conditions, not just the changes in 21(b). Moreover, the district 

court determined that the Corps took a hard look at the entire record before 

reaching its CWA and NEPA determinations, and that the decision to treat 

grandfathered-in permits under 21(a) differently than new permits under 21(b) was 

not arbitrary and capricious because the Corps considered the permit as a whole in 

making its finding of no significant impact. 

Riverkeeper timely appealed to this Court for the second time. 

II.

“We review the district court’s decision to grant summary judgment to the 

Corps and the Intervenors on the merits de novo, while applying the appropriate 

standard of review to the agency’s decision.” Black Warrior Riverkeeper, 781 

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22

F.3d at 1288. We review the Corps’ permitting decisions, as well as its Finding of 

No Significant Impact and decision not to prepare an Environmental Impact 

Statement pursuant to NEPA, under the Administrative Procedure Act’s arbitrary 

and capricious standard. Black Warrior Riverkeeper, 781 F.3d at 1288. Under the 

Administrative Procedure Act, we must “hold unlawful and set aside agency 

action, findings, and conclusions found to be . . . arbitrary, capricious, an abuse of 

discretion, or otherwise not in accordance with law.” 5 U.S.C. § 706. The 

arbitrary and capricious standard is a highly deferential one, and we cannot 

substitute our judgment for that of the agency as long as the agency’s conclusions 

are rational and reasonably explained. Sierra Club v. Van Antwerp, 526 F.3d 

1353, 1360 (11th Cir. 2008). Our inquiry is limited by law to whether the agency’s 

decision was based on a consideration of the relevant factors and, ultimately, 

whether it made a clear error of judgment. Fund for Animals, Inc. v. Rice, 85 F.3d 

535, 541 (11th Cir. 1996). Our deference extends both to an agency’s ultimate 

findings as well as “drafting decisions like how much discussion to include on each 

topic, and how much data is necessary to fully address each issue.” Van Antwerp, 

526 F.3d at 1361. While we should “uphold a decision of less than ideal clarity if 

the agency’s path may reasonably be discerned,” Bowman Transp., Inc. v. Ark.-

Best Freight Sys., Inc., 419 U.S. 281, 286 (1974), “[w]e may not supply a reasoned 

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23

basis for the agency’s action that the agency itself has not given,” Motor Vehicle 

Mfrs. Ass’n v. State Farm Mut. Auto. Ins. Co., 463 U.S. 29, 43 (1983). 

Our task ultimately is to “ensure that the agency took a ‘hard look’ at the 

environmental consequences of the proposed action.” Sierra Club v. U.S. Army 

Corps of Eng’rs, 295 F.3d 1209, 1216 (11th Cir. 2002). An agency has satisfied 

the “hard look” requirement if it has “examine[d] the relevant data and 

articulate[d] a satisfactory explanation for its action including a rational connection 

between the facts found and the choice made.” Id. (quotation marks omitted).

III.

A.

In view of the substantial deference we afford agency action, Riverkeeper 

faces an upstream swim. It renews its “disparate treatment” argument, contending 

again that the Corps’ CWA and NEPA determinations are arbitrary and capricious 

because the Corps determined that the new 1⁄2-acre and 300 linear-foot limits

imposed on permits under 21(b) are necessary to ensure minimal environmental 

impact, but declined to impose any of those new limitations on the grandfatheredin permits under 21(a).4

 In other words, Riverkeeper says that the activities 

authorized under 21(a) cannot possibly result in minimal impact to navigable 

 4 Riverkeeper concedes that the Revised Decision Document fixed the Corps’ previous 

underestimation error that prevented us from reaching the merits the first time around, and agrees 

that error is no longer a legal issue in the case. 

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waters because they are not subject to the very limitations that the Corps itself 

deemed necessary to ensure minimal impact. It observes that 41 of the 88 

authorizations under 21(a) are located in the Black Warrior River Watershed, and 

those 41 authorizations will allow an additional 25 miles of stream impacts that 

would not occur if they were subject to the limitations found in 21(b). Therefore, it

asks us to vacate the grandfather provision in NWP 21(a) and all of the 

authorizations issued thereunder. Ultimately, we find that Riverkeeper’s 

arguments can’t swim against the tide.

For starters, we think that the text of NWP 21(a) goes a long way to 

supporting the Corps’ determination that authorized activities under 21(a) will 

have minimal individual and cumulative adverse effects. NWP 21(a) provides that 

a previously authorized mining activity under the 2007 NWP 21 can only be 

reauthorized under 21(a) if a district engineer determines that: the activity does not 

create any greater “loss of waters” than it did under the 2007 permit; the activity 

“will result in minimal individual and cumulative adverse effects”; and it complies 

with additional “applicable regional conditions and any activity-specific conditions 

added to the NWP authorization by the district engineer, such as compensatory 

mitigation requirements.” Reissuance of Nationwide Permits, 77 Fed. Reg. at 

10,274 (emphasis added). These explicit requirements apply to all 21(a) 

authorizations and substantially undercut Riverkeeper’s argument that the new 

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21(b) limitations are the only way that the Corps can ensure minimal individual

and cumulative adverse environmental effects. On its face, Rule 21(a) expressly 

requires a district engineer to determine that a grandfathered-in permit will have 

minimal effects before authorizing it. Riverkeeper has not provided any reason to 

believe that NWP 21(a) will fail to operate according to its terms, or that the 

district engineers will abandon the many tasks they are obliged to perform.

In fact, the Revised Decision Document explains that NWP 21(a) will 

operate exactly as the text suggests it will: “For those previously authorized 

surface coal mining activities, the district engineer must determine that the activity 

continues to result in minimal individual and cumulative adverse effects on the 

aquatic environment.” The Revised Decision Document later emphasizes that 

NWP 21(a) activities must be confirmed by the district engineer to “result[] in 

minimal individual and cumulative adverse effects on the aquatic environment,”

and that the district engineer can revise any applicable regional conditions and 

activity-specific conditions, including compensatory mitigation requirements, “if 

the existing ones are determined not to be adequate to ensure minimal adverse 

effects.” And, indeed, if the district engineer determines that the cumulative 

adverse effects of NWP 21-authorized activities are more than minimal in a 

“specific watershed” (such as the Black Warrior River Watershed), they are 

authorized to require individual permits or add conditions to the NWP on a caseUSCA11 Case: 15-14745 Date Filed: 08/12/2016 Page: 25 of 35
26

by-case basis. Finally, the Revised Decision Document reiterates what the text of 

NWP 21(a) should make clear: if a previously verified activity is expanded in such 

a way that it will “result in greater losses of waters of the United States,” it cannot 

be authorized under NWP 21 unless it qualifies under NWP 21(b). Thus, from the 

explicit restrictions placed on activities under 21(a), it naturally follows that 21(a) 

authorizations will have minimal environmental impact.

Moreover, the Corps considered both the 21(a) and (b) authorizations in 

evaluating whether the permits met the CWA’s and NEPA’s minimal impact 

requirements. The Revised Decision Document makes it abundantly clear 

throughout that the minimal impact analysis is based on both 21(a) and (b) 

activities:

The estimated contribution of this NWP to the cumulative effects to 

aquatic resources in the United States during the five year period that 

the NWP would be in effect, in terms of the estimated number of time 

this NWP would be used until it expires and the projected impacts and 

compensatory mitigation, is provided in Section 6.2.2. The activities 

authorized by this NWP, including the activities authorized under 

paragraphs (a) and (b) of this NWP, will result in a minor incremental 

contribution to the cumulative effects that have occurred to wetlands, 

streams, and other aquatic resources in the United States because, as 

discussed in this section, they are one of many activities that affect 

those resources. 

The Corps’ minimal impact analysis plainly considered data for “all of the NWP 

21(a) verifications that could be issued during the period [the 2012] NWP 21 is in 

effect,” which was available at the time of the Revised Decision Document 

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“because the terms of NWP 21(a) state that those verifications should generally be 

issued on or before March 18, 2013,” and the Revised Decision Document was 

produced in August 2015. Thus, it seems to us that the Corps considered the 

relevant factors in performing its environmental impact analysis.

Riverkeeper does not contest the accuracy of the environmental impact 

estimates provided by the Corps, nor does it explain why the actual acreage 

impacts of projects under 21(a) -- for which the Corps had confirmed data at the 

time it drafted the Revised Decision Document -- are more than “minimal” as that 

term is used in the Clean Water Act. Rather, it invites us to parse the language of 

the Revised Decision Document for statements suggesting that 21(b)’s 1⁄2-acre and 

300 linear-foot limits are the only means of ensuring minimal environmental 

impact. As we recounted above, there are a few statements in the Revised 

Decision Document that suggest that the 21(b) limitations are “necessary” to 

ensure minimal environmental impacts. But, under arbitrary and capricious 

review, we must “uphold a decision of less than ideal clarity if the agency’s path 

may reasonably be discerned.” Bowman Transp., Inc., 419 U.S. at 286. And we 

have no trouble discerning that the Corps considered the limitations imposed under 

both sections of NWP 21, as well as general permit conditions applicable to all 

NWPs in reaching its environmental impact determinations. 

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In estimating the environmental impact of the new NWP 21, the Corps

assessed “individual and cumulative effects” by considering “the terms and limits 

of the NWP, pre-construction notification requirements,[5

] and the standard NWP 

general conditions.” The Revised Decision Document repeatedly states that the

Corps’ environmental impact determinations were based on both 21(a) and (b) 

activities and the wide array of means available to limit the impact of activities 

under both provisions. Specifically, it noted that “the imposition of the 1⁄2-acre 

limit, 300 linear foot limit, and prohibition against authorizing valley fills on 

activities that were not previously authorized under the 2007 NWP 21, as well as 

the pre-construction notification requirements and other procedural safeguards, 

will authorize only those activities with minimal individual and cumulative adverse 

effects on the aquatic environment.” These “other procedural safeguards include 

the authority for division engineers to modify, suspend, or revoke NWP 21 

authorizations on a regional basis, and the authority for district engineers to modify 

NWP 21 authorizations by adding conditions, such as compensatory mitigation 

requirements, to ensure minimal individual and cumulative adverse effects on the 

aquatic environment.”

 5 Pre-construction notification involves evaluating proposed activities to determine 

whether they result in minimal individual and cumulative adverse effects on the aquatic 

environment, and whether compensatory mitigation is needed to comply with the minimal 

adverse environmental effects requirement for general permits. 

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The Revised Decision Document elaborates that “[c]ompensatory mitigation 

required for activities verified under the 2007 NWP 21 [i.e., the 2012 

grandfathered activities under 21(a)] will continue to be required, and may be 

augmented if the district engineer determines that they do not adequately 

compensate for losses of aquatic resource function and ensure minimal adverse 

effects.” In fact, the Corps’ ultimate “minimal impact” finding explicitly 

referenced all of the limits that NWP 21 imposes on permitted activities, not just 

those contained in 21(a): “Compliance with the terms and conditions of this NWP, 

including the mitigation general condition (general condition 23), as well as 

compliance with regional conditions imposed by division engineers and activityspecific conditions added to NWP verifications by district engineers, will ensure 

that the activities authorized by this NWP will result in no more than minimal 

individual and cumulative adverse effects on the aquatic environment.” Thus, it 

seems plain to us that the Corps took a hard look at the environmental impact of 

authorizations under both 21(a) and (b), and determined that the restrictions 

imposed on each set of authorizations were sufficient to ensure that they result in 

no more than minimal individual and adverse cumulative effects.

Throughout the Revised Decision Document, the Corps placed special 

reliance on compensatory mitigation as a means of ensuring minimal net 

environmental impacts. Riverkeeper criticizes the Corps’ reliance on 

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compensatory mitigation as a “simplistic calculation” based on the erroneous 

assumption that compensatory mitigation will always fully offset the adverse 

environmental impacts of dumping surface spoil in streams.6

 But nothing in the 

Revised Decision Document suggests that the Corps’ relied on compensatory 

mitigation to fully offset the environmental impacts of permitted activities --

indeed, the Corps’ analysis suggests that compensatory mitigation is simply one of 

many restrictions applicable to 21(a) and (b) authorizations that will help to ensure 

that NWP 21 authorizations meet statutory requirements. The Corps candidly 

conceded in the Revised Decision Document that “it is difficult to assess whether 

compensatory mitigation has fully or partially offset the lost functions provided by 

the aquatic resources that are impacted by permitted activities,” but determined 

that so long as its general guidelines are followed, compensatory mitigation “will 

provide aquatic resource functions and services to offset some or all of the losses 

of aquatic resource functions caused by the activities by this NWP, and reduce the 

 6 In Kentucky Riverkeeper, Inc. v. Rowlette, 714 F.3d 402 (6th Cir. 2013), the Sixth 

Circuit invalidated NWP 21(a) as arbitrary and capricious, id. at 413, because the Corps had 

failed to comply with its own regulations requiring the Corps to provide analysis or 

documentation to support its determination that compensatory mitigation will ensure minimal 

adverse effects, id. at 411 (citing 40 C.F.R. §§ 230.7(b), 230.11). For the first time in its reply 

brief, Riverkeeper argued that the Corps’ failure to provide adequate documentation in support of 

its compensatory mitigation analysis ran afoul of 40 C.F.R. § 230.7(b). However, “[a]rguments 

raised for the first time in a reply brief are not properly before a reviewing court.” Herring v. 

Sec’y, Dep't of Corr., 397 F.3d 1338, 1342 (11th Cir. 2005) (quotation omitted).

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contribution of those activities to the cumulative effects on the Nation’s wetlands, 

streams, and other aquatic resources.” 

Moreover, we must afford the Corps special deference in this area because it 

“is making predictions, within its area of special expertise, at the frontiers of 

science . . . as opposed to simple findings of fact.” Miccosukee Tribe, 566 F.3d at

1264. As evidenced by the numerous scientific research papers discussed in the 

Revised Decision Document, the minimum impact analysis involves difficult 

predictions about how coal mining activities will affect complex ecosystems, and 

how district engineers will be able to offset those effects through permit-specific 

requirements and compensatory mitigation. This is not an area where we may

easily second-guess the Corps, especially considering that Riverkeeper has not 

contested any of the Corps’ data or even argued that its estimates exceed 

“minimal” impact as that term is used in the CWA. For all of these reasons, we 

find that the Corps’ environmental impact findings under the CWA and NEPA 

were not arbitrary and capricious.

B.

Relatedly, the Riverkeeper claims that the Corps has not articulated a 

sufficient rationale for treating similar mining activities differently under NWP 

21(a) and (b). See Yetman v. Garvey, 261 F.3d 664, 669 (7th Cir. 2001) (“A long 

line of precedent has established that an agency action is considered arbitrary when 

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the agency has offered insufficient reasons for treating similar cases differently.”). 

It argues that the only reason for the differential treatment is to alleviate the coal 

mining companies’ financial burden of obtaining individual permits, which 

Riverkeeper maintains is not a permissible consideration under the Clean Water 

Act. We remain unpersuaded.

Riverkeeper is correct that one of the Corps’ principal justifications for 

grandfathering in 21(a) permits was economic hardship to the regulated companies. 

Indeed, the Revised Decision Document acknowledged that the purpose of 

including the grandfather provision under 21(a) was “to reduce hardships on 

permittees who previously obtained authorization under the NWP 21 issued on 

March 12, 2007, and invested substantial resources in reliance on that NWP 

authorization,” while also protecting the aquatic environment. We also agree with 

Riverkeeper that -- as the Corps concedes -- the Corps could not rely on economic 

considerations to issue a general permit that does not comply with the Clean Water 

Act’s minimal impact requirements. 

Nevertheless, Riverkeeper’s argument is unpersuasive. For starters, the

Corps was not required to impose identical restrictions on applications under the 

two provisions of NWP 21. The Clean Water Act requires only that the activities 

governed by a general permit are “similar in nature, will cause only minimal 

adverse environmental effects when performed separately, and will have only 

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minimal cumulative adverse effects on the environment.” 33 U.S.C. § 1334(e)(1). 

As we’ve explained already, there is nothing arbitrary or capricious about the 

Corps’ decision that activities under both NWP 21(a) and (b) will have minimal 

individual and cumulative adverse impacts, and Riverkeeper does not contend that 

the two groups of activities are insufficiently similar in nature to be encompassed 

by a general permit. Under arbitrary and capricious review, we may set aside the 

Corps’ decision “only for substantial procedural or substantive reasons as 

mandated by statute”; we may not erect non-statutory dams to impede the Corps’

discretion. Fund for Animals, 85 F.3d at 542 (emphasis added) (quoting N.

Buckhead Civic Ass’n v. Skinner, 903 F.2d 1533, 1539 (11th Cir. 1990)). Nothing 

in the CWA or NEPA precluded the Corps from relying on economic 

considerations in choosing between alternatives that have minimal aquatic impacts

in order to ensure that mining companies were not unfairly burdened by the new 

permit requirements.

Moreover, the Revised Decision Document evinces an additional, reasonable 

basis for treating authorizations under 21(a) and (b) differently. Paragraph (a) only 

applies to a well-defined and limited subset of activities that can be reliably

verified to have minimal environmental impact. At the time that it drafted the 

2012 NWP 21, the Corps knew the entire universe of potential projects under 21(a) 

because they had all already been operating for five years by that time, and, 

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notably, by the time that it drafted the Revised Decision Document, it had impact 

data for “all of the NWP 21(a) verifications that could be issued during the period 

[the 2012] NWP 21 is in effect.” In contrast, for new projects under 21(b), the 

Corps had to rely on estimates of potential use over the five year term. In fact, the 

Revised Decision Document cited “the difficulty of documenting minimal adverse 

effect determinations for losses of aquatic resource area and functions that exceed 

those allowed in other NWPs” as a reason for moving away from preconstruction 

review and instead imposing strict caps on new projects. But that difficulty is 

substantially less relevant for grandfathered-in permits that had already been 

operating for years at the time that NWP 21 was issued. The Corps reasonably 

concluded that this subset of projects presents less of a risk of harm to the aquatic 

environment, while deciding to hold new -- and, therefore, more unpredictable --

projects to a different, and higher, standard.7

 We find that the Corps has provided

a “satisfactory explanation for its action” based on its findings in the Revised 

Decision Document, so we will (as we must) defer to its decision. State Farm, 463 

U.S. at 42-43.

 7 As we noted earlier, in 2010, the Corps suspended the 2007 NWP 21 for mining 

activities in six Appalachian states. The Revised Decision Document provides that activities that 

were subject to the 2010 suspension may not apply for authorization under 21(a), and must either 

seek individual permits or fit within the 21(b) limits. This further supports the Corps’ reasonable 

judgment to treat 21(a) and (b) activities differently, as 21(a) activities are already a less risky 

subset of the prior NWP 21 activities.

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The long and short of it is, there was nothing arbitrary and capricious about 

the Corps’ decision to treat old and new activities differently under the two 

provisions of this Nationwide Permit, or in its finding that the activities authorized 

under both provisions would result in minimal individual and cumulative impacts 

to the aquatic environment. Accordingly, we affirm the judgment of the district 

court granting final summary judgment to the Corps.

AFFIRMED.

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