JOHN D. BATES, United States District Judge.
Plaintiffs, three New Hampshire cities, filed this action pursuant to the citizen-suit
Last year, this Court granted defendants' motion to dismiss plaintiffs' complaint, dismissing it with prejudice for failure to state a claim under Federal Rule of Civil Procedure 12(b)(6). July 30, 2013 Order [ECF No. 18]. Plaintiffs own and operate waste treatment plants that discharge into the Great Bay Estuary, and they challenged several regulatory decisions made by EPA that they believe affected their ability to continue to do so. In rejecting plaintiffs' arguments that EPA acted improperly, the Court noted in dicta that plaintiffs might have raised their challenge to EPA's actions in the context of an APA challenge to certain decisions that EPA made. See July 30, 2013 Mem. Op. [ECF No. 17] ("Mem.Op.") 15 (noting that "plaintiffs' real argument ... is that the EPA ... [has] improperly given [a certain report] the force of law in subsequent decisions" and that plaintiffs' "challenge must be raised in the context of those subsequent decisions"). Plaintiffs, seeing this language as an invitation, moved under Fed. R. Civ. P. 59(e) and 15(a) to reopen the judgment and to amend their complaint to assert an APA claim, and the Court granted that motion. See Nov. 15, 2013 Mem. Op. & Order [ECF No. 27]. After plaintiffs amended their complaint, EPA again moved to dismiss the complaint. The Court will grant that motion because, in effect, plaintiffs still have not chosen the proper decisions to challenge.
The Court is mindful that, assuming plaintiffs' allegations are true, they may someday be forced to expend significant resources to comply with EPA's directives. That day is not today, however, which is the central flaw in their case. The regulatory decisions that plaintiffs challenge have not yet caused them harm, and indeed whether plaintiffs will be harmed is still uncertain. They ask the Court to tell EPA that it acted improperly when listing the Great Bay Estuary waters as impaired, or polluted. But EPA's action does not mean plaintiffs have to change their behavior today. And even if EPA had never listed those waters as impaired, plaintiffs might have to change their behavior anyway because of a separate permitting process. So even if plaintiffs are right that EPA acted improperly, taking the waters off the list will not help them. Down the road, plaintiffs may receive permits that do force them to spend money, whether or not the waters are listed as impaired. When they do, by statute, plaintiffs will have to challenge those permits in another forum. See 33 U.S.C. § 1369(b). This Court also cannot review actions that EPA and New Hampshire have yet to take, such as the issuance of a total maximum daily load for the Great Bay Estuary and the issuance of a new general stormwater permit. Moreover, plaintiffs do not have a right to participate in EPA's listing decision, so when EPA excluded them from that decisionmaking process, plaintiffs lost nothing to which they were entitled. Plaintiffs may yet have their day in court, but they have simply picked the wrong day.
EPA asserts two grounds for dismissal, arguing that plaintiffs do not have standing to bring their claims and that their claims are not ripe. See Defs.' Mem. in Supp. of Mot. to Dismiss [ECF No. 32-1] ("Defs.' Mot.") 1. These are challenges to this Court's subject-matter jurisdiction and therefore will be evaluated under Fed. R. Civ. P. 12(b)(1). See Haase v. Sessions, 835 F.2d 902, 906 (D.C.Cir.1987) (stating that "the defect of standing is a defect in subject matter jurisdiction"). "[I]n passing on a motion to dismiss, whether on the ground of lack of jurisdiction over the subject matter or for failure to state a cause of action, the allegations of the complaint should be construed favorably to the pleader." Scheuer v. Rhodes, 416 U.S. 232, 236, 94 S.Ct. 1683, 40 L.Ed.2d 90 (1974); see also Leatherman v. Tarrant Cnty. Narcotics Intel. & Coord. Unit, 507 U.S. 163, 164, 113 S.Ct. 1160, 122 L.Ed.2d 517 (1993). Therefore, the factual allegations must be presumed true, and plaintiffs must be given every favorable inference that reasonably may be drawn from the allegations of fact. See Scheuer, 416 U.S. at 236, 94 S.Ct. 1683; Sparrow v. United Air Lines, Inc., 216 F.3d 1111, 1113 (D.C.Cir.2000). The Court need not, however, accept as true "a legal conclusion couched as a factual allegation," nor inferences that are unsupported by the facts set out in the complaint. Trudeau v. FTC, 456 F.3d 178, 193 (D.C.Cir.2006) (quoting Papasan v. Allain, 478 U.S. 265, 286, 106 S.Ct. 2932, 92 L.Ed.2d 209 (1986)).
Although courts examining a Rule 12(b)(1) motion to dismiss—such as for lack of standing or ripeness—will "construe the complaint in favor of the complaining party," see Warth v. Seldin, 422 U.S. 490, 501, 95 S.Ct. 2197, 45 L.Ed.2d 343 (1975), the "`plaintiff's factual allegations in the complaint ... will bear closer scrutiny in resolving a 12(b)(1) motion' than in resolving a 12(b)(6) motion for failure to state a claim," Grand Lodge of Fraternal Order of Police v. Ashcroft, 185 F.Supp.2d 9, 13-14 (D.D.C.2001) (quoting 5A Charles Alan Wright & Arthur R. Miller, Federal Practice & Procedure § 1350 (2d ed.1987)). Because the elements necessary to establish jurisdiction are "not mere pleading requirements but rather an indispensable part of the plaintiff's case, each element must be supported in the same way as any other matter on which the plaintiff bears the burden of proof; i.e., with the manner and degree of evidence required at successive stages of the litigation." Lujan v. Defenders of Wildlife, 504 U.S. 555, 561, 112 S.Ct. 2130, 119 L.Ed.2d 351 (1992). Thus, a court may consider material other than the allegations of the complaint in determining whether it has jurisdiction to hear the case, so long as the court accepts the factual allegations in the complaint as true. See Jerome Stevens Pharms., Inc. v. FDA, 402 F.3d 1249, 1253-54 (D.C.Cir.2005); EEOC v. St. Francis Xavier Parochial Sch., 117 F.3d 621, 624-25 n. 3 (D.C.Cir.1997).
Generally, the Clean Water Act uses two different types of standards "to restore and maintain the chemical, physical, and biological integrity of the Nation's waters": technology-based standards and water-quality standards. 33 U.S.C. § 1251(a). Technology-based standards set a minimum level of treatment that must be performed by those who discharge pollutants into waters. That level is predetermined by EPA to be both technologically available and economically achievable. Id.
Water quality standards can be expressed as numerical criteria or as narrative criteria. 40 C.F.R. § 131.3(b). Numerical criteria define specific levels or concentrations of particular pollutants, while narrative criteria describe the body of water or levels of pollutants in qualitative terms. Whether expressed numerically or narratively, standards describe the maximum amount of pollutants that waters can contain before their designated use is considered to be impaired. For example, a water quality standard relating to a water supply might set a level of chlorine in parts per billion ("PPB"). Waters that contain levels of chlorine higher than, e.g., 20 PPB would be considered, under that water quality standard, impaired for use as a water supply. Narrative standards are less specific: for example, one might provide that bodies of water designated for use as water supplies shall not contain chlorine in concentrations that would impair their use as water supplies. Several parts of the Act's regulatory scheme call for EPA or a state to translate narrative criteria into numerical standards for some purpose.
Under the Act, certain sources (such as plaintiffs' waste treatment plants) may discharge pollutants only under the terms of a National Pollution Discharge Elimination System permit ("NPDES permit" or simply "permit"), which may be administered by a state or by EPA. See Am. Paper Inst., 996 F.2d at 349; see also 33 U.S.C. §§ 1311(a), 1342.
Permits are waterway- and discharger-specific. Permits limit those who discharge pollutants into particular waterways by limiting the amount of a particular pollutant a permitholder may release (often referred to as "effluent limits"). Those limits are set with reference to the waterway into which the permitholder is releasing pollutants. If the applicable water quality standard for a particular waterway is strict, a permitholder likely will face strict limits on how much of a particular pollutant it can release into that waterway.
Permits contain both technology-based limits and water-quality-based limits. 33 U.S.C. §§ 1311(b), 1314(b). Technology-based limits essentially act as a floor: they describe a minimum level of treatment a permitholder must perform. Permitholders must meet both technology-based limits and water-quality-based limits. If technology-based limits are not strict enough to ensure that a state's water quality standards
NPDES permits are but one piece of the Act's larger scheme designed to protect the nation's waters. Another piece of that scheme is provided in 33 U.S.C. § 1313(d) (section 303(d) of the Act). Under that provision, every two years, each state must identify and list waters for which technology-based limits are not strict enough to achieve or maintain state water quality standards. 40 C.F.R. § 130.7; see 33 U.S.C. § 1313(d)(2). In creating its section 303(d) list, a state must "assemble and evaluate all existing and readily available water quality-related data and information." 40 C.F.R. § 130.7(b)(5). EPA must then approve or disapprove of that list, referred to as the "impaired waters list" or the "303(d) list." 33 U.S.C. § 1313(d)(2) (EPA must establish its own list if it disapproves of state's list). To sum up, waters are included on the 303(d) list if technology-based standards alone are not enough to achieve state water quality standards, while permits must contain limits sufficient to achieve state water quality standards.
For each body of water on the 303(d) list, a state must establish a "total maximum daily load" ("TMDL") for each pollutant that is "preventing or [is] expected to prevent attainment of water quality standards." 40 C.F.R. § 130.7(c)(1)(ii); see 33 U.S.C. § 1313(d)(1)(C). Essentially, a TMDL is a "pollution budget" for each body of water. It sets a cap on the total amount of, say, chlorine that can be added to a body of water from all sources per day before it will no longer meet state water quality standards. As with the 303(d) list, EPA must approve or disapprove of TMDLs established for waters on the 303(d) list. 33 U.S.C. § 1313(d)(2) (EPA must establish its own TMDLs if it disapproves of state's TMDLs).
But a TMDL "does not, by itself, prohibit any conduct or require any actions. Instead, each TMDL represents a goal that may be implemented by adjusting pollutant discharge requirements in individual NPDES permits or establishing nonpoint source controls."
Taking as true the allegations in the complaint, as the Court must at this stage, see Oberwetter v. Hilliard, 639 F.3d 545, 549 (D.C.Cir.2011), the following facts form the basis for this action. New Hampshire has narrative water quality criteria, and EPA administers the NPDES permits for New Hampshire waters. See 33 U.S.C. § 1342(a), (b); see also Defs.' Reply in Supp. of Mot. to Dismiss [ECF No. 39] ("Defs.' Reply") 1 n.1. In relevant part, New Hampshire's water quality standards provide that certain "waters shall contain no ... nitrogen in such concentrations that would impair any existing or designated uses, unless naturally occurring"; that "[e]xisting discharges containing... nitrogen which encourage cultural eutrophication
After conducting a site-specific water quality analysis of the Great Bay Estuary waters (the waters at issue here), working closely with EPA, and receiving public comments, the New Hampshire Department of Environmental Services ("NHDES") published a report ("the 2009 Document") "contain[ing] proposals for numeric nutrient criteria for different designated uses in the Great Bay Estuary." Ex. 1 to Compl. [ECF No. 1-1] 74 ("2009 Document"). Put differently, the 2009 Document contains proposed translations of New Hampshire's narrative standards into numeric values. As explained in the Court's previous opinion, however, the 2009 Document is not itself a state water quality standard. Mem. Op. at 10.
Plaintiffs, who operate waste treatment facilities that discharge into the Great Bay Estuary under NPDES permits, think that the maximum nitrogen levels proposed in the 2009 Document are too low. Thus, when NHDES and EPA allegedly relied on that document to interpret New Hampshire's narrative water quality criteria, and placed the Great Bay Estuary waters on the impaired waters list because it had nitrogen levels above those maximum levels, plaintiffs took issue.
EPA counters that the presence of the Great Bay Estuary waters on the impaired waters list did not, and will not, cause the effects of which plaintiffs complain. Accordingly, EPA contends that plaintiffs have no standing to challenge the impaired waters listing determination, arguing that plaintiffs cannot demonstrate any injury caused by the 303(d) listing decision that is redressable by removing the waters from the list. EPA also argues that the case is not ripe for this Court's review.
Standing is a "threshold question in every federal case." Warth, 422 U.S. at 498, 95 S.Ct. 2197. Article III of the U.S. Constitution "limits the `judicial power' of the United States to the resolution of `cases' and `controversies,'" Valley Forge Christian Coll. v. Am. United for Separation of Church & State, Inc., 454 U.S. 464, 471, 102 S.Ct. 752, 70 L.Ed.2d 700 (1982), and the doctrine of standing serves to identify those "`Cases' and `Controversies' that are of the justiciable sort referred to in Article III" and which are thus "`appropriately resolved through the judicial process,'" Lujan, 504 U.S. at 560, 112 S.Ct. 2130 (quoting Whitmore v. Arkansas, 495 U.S. 149, 155, 110 S.Ct. 1717, 109 L.Ed.2d 135 (1990)). "In essence the question of standing is whether the litigant is entitled to have the court decide the merits of the dispute or of particular issues." Warth, 422 U.S. at 498, 95 S.Ct. 2197. To establish the "irreducible constitutional minimum of standing," a plaintiff must allege (1) an "injury in fact" which is "(a) concrete and particularized and (b) actual or imminent, not conjectural or hypothetical"; (2) "a causal connection between the injury and the conduct complained of"; and (3) a likelihood "that the injury will be redressed by a favorable decision." Lujan, 504 U.S. at 560-61, 112 S.Ct. 2130 (internal quotation marks and citations omitted). Plaintiffs assert injuries in four areas: new NPDES permits with restrictive nitrogen limits, restrictions on the expansion of their facilities, increased costs due to a general stormwater permit, and a due process injury. None will support Article III standing.
Plaintiffs assert that, "[a]s a result of EPA's [approval of Great Bay Estuary waters being included on the 303(d) list], the Cities received (or have been expressly informed that they will receive) NPDES permits ... that, for the first time, will contain extremely restrictive effluent [nitrogen] limitations." Pls.' Opp'n at 1-2. That hedge (that the Cities "have been expressly informed that they will receive" restrictive permits) is important: none of the plaintiffs have actually been issued a final NPDES permit with the nitrogen limits to which plaintiffs take exception. Plaintiffs try to brush off this critical fact by noting that "two Great Bay wastewater treatment facilities have already been issued final NPDES permits that impose these extremely restrictive [nitrogen] limitations." Id. at 2 n.1. But neither of those facilities is operated by plaintiffs. Instead, they are owned and operated by two cities that are not plaintiffs in this action, Exeter and Newmarket. Id. at 2 n.1, 6. Plaintiffs go on to note that "[t]he City of Dover [an actual plaintiff] has been issued a draft permit
Plaintiffs contend that, by approving the inclusion of the Great Bay Estuary waters on the 303(d) list, EPA immediately caused them significant injury. In plaintiffs' view, once EPA included those waters on the impaired list, it was required by its own regulations to issue plaintiffs permits with more restrictive nitrogen limits. Id. at 11 ("According to EPA's own regulations, these permits must require pollutant reductions if the permittee discharges the pollutant of concern ... to the waterbody identified as impaired on the 303(d) list.") (emphasis added); id. at 13 ("presence on the [303(d)] list guarantees" that a permit will contain a limit) (emphasis added). Plaintiffs believe that this requirement kicked in the moment that EPA put the waters on the impaired list. Id. at 10 (citing "direct and immediate impact" of EPA's 303(d) approvals on permitting process).
To refresh, waters are included on the 303(d) list if the technology-based limits required by other sections of the CWA (§§ 1311(b)(1)(A) and (b)(1)(B)) "are not stringent enough to implement any water quality standard applicable to such waters." 33 U.S.C. § 1313(d)(1)(A). NPDES permits, meanwhile, must contain water-quality-based standards sufficient to "[a]chieve water quality standards established under [33 U.S.C. § 1313], including State narrative criteria for water quality." 40 C.F.R. § 122.44(d)(1). Specifically, those standards must control all pollutants that "are or may be discharged at a level which will cause, have the reasonable potential to cause, or contribute to an excursion above any State water quality standard, including State narrative criteria for water quality." Id. § 122.44(d)(1)(i).
If EPA
Plaintiffs assert that the 303(d) list determination and NPDES permitting decisions are inextricably intertwined, so that "if a waterbody has already been identified as impaired on the 303(d) list as not meeting `applicable standards,' the [excursion above the state water quality standard] is already established and the permit writer simply calculates and imposes an effluent limitation." Pls.' Opp'n at 4. In effect, plaintiffs conceive of 303(d) listing as a regulatory shortcut: they believe it conclusively establishes that a pollutant is a concern under the reasonable potential determination, and that EPA must therefore calculate and establish limits for that pollutant.
But this shortcut does not exist. The permitting regulation explains that, "[w]hen determining whether a discharge causes, has the reasonable potential to cause, or contributes to an in-stream excursion above a narrative or numeric criteria within a State water quality standard, [EPA] shall use procedures which account for" several different factors, none of which is 303(d) listing. 40 C.F.R. § 122.44(d)(1)(ii) (EPA must account for existing controls on sources of pollution, variability of the pollutant in the discharge, sensitivity of the species to toxicity testing, and dilution of effluent in water). Simply put, the 303(d) listing determination and the section 122.44(d)(1)(i) determination are wholly separate. Hence, to make the 303(d) list determination, EPA asks whether a particular body of water is polluted; to make the section 122.44(d)(1)(i) reasonable potential determination, EPA asks whether a particular source is discharging too much of a pollutant.
Plaintiffs themselves pithily reveal their causation problems when they write that "without the 303(d) decision approvals, EPA could not impose [nitrogen] limitations under 40 C.F.R. § 122.44(d), unless it independently determined that the Cities' nitrogen discharges were causing or contributing to violations of the state's narrative criteria (the true "applicable standard)." Pls.' Opp'n at 21 (emphasis added). Indeed. They also explain that "[t]his permitting regulation—[section] 122.44(d)—applies regardless of whether the TMDL has been developed." Pls.' Opp'n at 4. Plaintiffs describe very well the regulatory process at work: under section 122.44(d), if EPA "independently determine[s]" that plaintiffs' facilities have the reasonable potential to cause the Great Bay Estuary waters to exceed New Hampshire's water quality standards, it must impose nitrogen limits in plaintiffs' NPDES permits. The independent determination that they mention is actually a determination EPA is required to make under section 122.44(d) when issuing permits. And just as section 122.44(d) applies
This is not to say that 303(d) lists never affect permitting decisions—they just do so indirectly. Plaintiffs leap past an intermediate step. When a body of water is placed on the 303(d) list, the state must establish a TMDL for that body of water for pollutants that are "preventing or expected to prevent attainment of water quality standards." 40 C.F.R. § 130.7(c)(1)(ii); 33 U.S.C. § 1313(d)(1)(C). This is not an immediate process, however.
Once a TMDL is issued, it certainly can affect NPDES permits. When developing water-quality-based standards for those permits, EPA must ensure that those standards are "consistent with" the applicable TMDL. Id. § 122.44(d)(1)(vii). So, once a TMDL has been promulgated, the process for establishing water-quality-based standards in permits includes this step in addition to the reasonable potential determination. In this way, the promulgation of a TMDL for a particular body of water might affect the permits for each point source discharging into that body of water.
Here, New Hampshire has not established a nitrogen TMDL for the Great Bay Estuary waters. New Hampshire is obliged to do so, now that the waters are on the 303(d) list, but it does not have to do so within a particular time limit. Permitting decisions cannot take into consideration a TMDL that has not yet been promulgated. Hence, between the 303(d) listing decision and the permitting decisions lies another decision—one made by New Hampshire, not the EPA, and one in which plaintiffs may participate, and of which they may seek review. See 40 C.F.R. § 130.7(c)(1)(ii). Plainly, the simple fact of 303(d) listing does not "guarantee" more stringent nitrogen limits in plaintiffs' permits, much less guarantee them "immediately": any limits will be required as a result of the TMDL, not because of the 303(d) listing, and the uncertainty surrounding the as-yet-unpromulgated TMDL precludes any "guaranteed" conclusions. Pls.' Opp'n at 10, 13.
The 303(d) list also may affect permitting decisions in another indirect way, again involving an intermediate step. Plaintiffs are correct that EPA can and does consider 303(d) listing when making its reasonable potential determination. Pls.' Opp'n at 6 (limits in proposed and "promised" permits "based on the 303(d) impairment determination"). While the 303(d) listing might therefore make it more likely that plaintiffs will receive a permit with restrictive nitrogen limits, it by no means guarantees it. As explained above, the reasonable potential determination is complex and involves many factors. In the permit issued to a non-plaintiff city that discharges into the Great Bay Estuary waters, EPA explains at length the many bases for its decision. See Defs.' Reply Ex. 6, Newmarket Permit Fact Sheet, at 25-31. It does mention the 303(d) listing, but careful review makes it clear that the listing was far from the only thing EPA considered. Although the
At bottom, even if plaintiffs have suffered an injury, the link between the 303(d) listing decision and plaintiffs' injury is too attenuated. See Allen v. Wright, 468 U.S. 737, 759, 104 S.Ct. 3315, 82 L.Ed.2d 556 (1984) ("The links in the chain of causation between the challenged ... conduct and the asserted injury are far too weak for the chain as a whole to sustain [plaintiffs'] standing."). Because the section 122.44(d) permitting process is not controlled by EPA's 303(d) listing decisions, plaintiffs cannot establish causation under Article III.
Plaintiffs counter with four cases in arguing that courts have granted review of 303(d) listings in similar situations. Those cases are all distinguishable. In the first two, Thomas v. Jackson, 581 F.3d 658 (8th Cir.2009), and American Canoe Association v. EPA, 30 F.Supp.2d 908 (E.D.Va. 1998), environmental groups challenged the omission of particular bodies of water from 303(d) lists. But in neither Thomas nor American Canoe Association did the deciding court address plaintiffs' standing to challenge the 303(d) listing decision.
Next, plaintiffs cite Florida Public Interest Research Group Citizen Lobby, Inc. v. EPA, 386 F.3d 1070 (11th Cir.2004) ("FPIR").
Plaintiffs also cite Barnum Timber Co. v. EPA, 633 F.3d 894 (9th Cir.2011). There, the court found that the landowner plaintiffs had standing because of an injury directly caused by the 303(d) listing of a waterbody on their land—the land depreciated in value. Id. at 898-901. Unlike plaintiffs in this case, the Barnum Timber plaintiffs did not challenge the 303(d) listing because of its perceived regulatory impact; rather, they showed that the very fact that waters on their land were on the list caused their property values to go down. Id. at 898. If the waters were taken off the list, their property value would go back up; hence, they could also show redressability. Id. at 901. Here, plaintiffs are concerned about the potential for restrictive permits. Whether those permits will contain restrictive limits is separate from whether the Great Bay Estuary waters are included on the 303(d) list. They have not yet received permits with restrictive limits, they cannot show that such restrictive limits would be caused by the 303(d) listing, and as explained below, reversing the listing decision would not prevent EPA from issuing restrictive permits.
Any injury related to the permits is not redressable. Even if the Great Bay Estuary waters were taken off the 303(d) list, nothing would require EPA to issue plaintiffs less restrictive permits. Indeed, because the limits in the permits to be received by plaintiffs are determined through a separate agency determination under section 122.44(d), those limits would be unaffected. Just as the 303(d) listing did not cause the proposed restrictive limits in plaintiffs' permits, reversing the listing will not ease those limits.
In short, plaintiffs' injury related to the permits is speculative, is not caused by EPA's decision to approve New Hampshire's 303(d) list, and is not redressable by overturning the listing decision. Hence, plaintiffs do not have standing to challenge that decision.
Plaintiffs next argue that the waters' inclusion on the 303(d) list harms
To qualify as a new source, plaintiffs' (hypothetical) expansion must be subject to performance standards under section 306 of the CWA. See id. § 122.2 (defining "new source"). Plaintiffs do not allege or argue that they are subject to those standards. Accordingly, any expansion would not qualify as a new source. Similarly, to qualify as a new discharger, plaintiffs' (hypothetical) expansion at the sites where they currently operate must have "never received a finally effective NDPES permit for discharges at that `site.'" See id. (defining "new discharger"). But plaintiffs have received finally effective NDPES permits.
In addition, plaintiffs' entirely hypothetical desire to expand cannot support standing. Plaintiffs do not allege, for example, that they have actual plans to expand their facilities and that the relevant regulations will prevent them from doing so. See Lujan, 504 U.S. at 564, 112 S.Ct. 2130 ("Such `some day' intentions—without any description of concrete plans, or indeed even any specification of when the some day will be—do not support a finding of the `actual or imminent' injury that our cases require."). Because the waters' inclusion on the 303(d) list does not preclude plaintiffs from expanding their facilities under section 122.4(i), and because any plans to do so are hypothetical, plaintiffs do not have standing based on section 122.4(i).
Plaintiffs next contend that they are injured by the 303(d) listing because it purportedly caused the EPA to issue what plaintiffs consider to be a restrictive general stormwater permit. They argue that "the minute EPA approved the 303(d) nutrient impairments for Great Bay and its tributaries, all of the Cities' various stormwater dischargers were presumed to be causing or contributing to the water quality exceedance and corrective measures were required for those sources also." Pls.' Opp'n at 8-9. But at "the minute EPA approved" the 303(d) lists at issue, EPA had issued only a draft revised stormwater permit for the State of New Hampshire connecting the 303(d) list with the stormwater permit. See 78 Fed.Reg. 9908, 9909, Draft "General Permits for Stormwater Discharges from Small Municipal Separate Storm Sewer Systems" (Feb. 2, 2013).
Plaintiffs' final standing argument is that they were injured because EPA deprived them of due process when it approved the 303(d) list. They contend that "EPA approved the 2009 amended [303(d)] list without affording the public the opportunity for notice and comment on this amended list, in violation of applicable rules," Pls.' Opp'n at 18,
What is more, they cannot establish that EPA's actions, even if they were procedural violations, deprived them of a protected liberty or property interest. See Gen. Elec. Co. v. Jackson, 610 F.3d 110, 117 (D.C.Cir.2010). Plaintiffs' allegations do not present a cognizable Article III injury. Put otherwise, a bare assertion of a procedural due process violation is not an Article III injury. Under settled precedent, plaintiffs do not have standing based simply on allegations that their due process rights have been violated. See Gen. Elec. Co., 610 F.3d at 117. The reason is straightforward: the Fifth and Fourteenth Amendments together guarantee
As explained above, the link between the 303(d) list approvals and EPA's permitting decisions under the NPDES system is simply too attenuated. Plaintiffs believe that the 303(d) list approvals have certain regulatory effects, but those regulatory effects are far from concrete. Inclusion on a 303(d) list will someday lead to the promulgation of a TMDL. That TMDL may someday lead to more restrictive permits. In the meantime, plaintiffs may receive restrictive permits because of an independent determination (made under a separate regulation—section 122.44(d)) that their current permits must limit the discharge of a particular pollutant. But until all that happens, the 303(d) list does not cause plaintiffs to suffer any injury. Hence, even if plaintiffs could identify a procedural violation (associated with the 303(d) list approval) that deprived them of due process rights, they cannot demonstrate that the violation deprived them of any protected liberty or property interest.
EPA also moves to dismiss because plaintiffs' claims are not ripe.
Because plaintiffs cannot show that they have standing under Article III, and because plaintiffs cannot demonstrate that the challenged decisions by EPA are ripe for review, the Court will dismiss plaintiffs' amended complaint. A separate order has issued on this date.
