Puerto Rico Aqueduct and Sewer Authority v. United States Environmental Protection Agency

35 F.3d 600, 39 ERC (BNA) 1269, 1994 U.S. App. LEXIS 23913, 1994 WL 462570
CourtCourt of Appeals for the First Circuit
DecidedAugust 31, 1994
Docket93-2340
StatusPublished
Cited by53 cases

This text of 35 F.3d 600 (Puerto Rico Aqueduct and Sewer Authority v. United States Environmental Protection Agency) is published on Counsel Stack Legal Research, covering Court of Appeals for the First Circuit primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Puerto Rico Aqueduct and Sewer Authority v. United States Environmental Protection Agency, 35 F.3d 600, 39 ERC (BNA) 1269, 1994 U.S. App. LEXIS 23913, 1994 WL 462570 (1st Cir. 1994).

Opinion

SELYA, Circuit Judge.

The United States Environmental Protection Agency (EPA), respondent before us, refused to hold an evidentiary hearing regarding its determination that a facility in Mayaguez owned by petitioner, Puerto Rico Aqueduct and Sewer Authority (PRASA), must fully meet the Clean Water Act’s secondary treatment requirements for publicly owned treatment works (POTWs). The gist of EPA’s decision was straightforward: having previously established secondary treatment requirements because PRASA’s POTW emitted pollutants into stressed waters, it determined that PRASA had failed to proffer any legally cognizable basis for modifying the requirements.

Petitioner now seeks judicial review of this determination. Its flagship objection demands that we place in bold relief the concept of administrative summary judgment. Petitioner’s less touted objections implicate the agency’s “stressed waters” standards. 1 Descrying no flaw in EPA’s application of either its procedural or substantive regulations, we affirm.

I. STATUTORY AND REGULATORY FRAMEWORK

Under the Clean Water Act, no pollutant may be emitted into this nation’s waters except in compliance with a National Pollution Discharge Elimination System (NPDES) permit. See 33 U.S.C. § 1311(a) (1988). Ordinarily, the NPDES permit issued to a POTW includes certain technology-based standards known as secondary treatment requirements. See id. § 1311(b)(1)(B). A POTW can obtain relief from these requirements by meeting nine separate criteria. These criteria are limned in 33 U.S.C. § 1311(h). They require the applicant to make various demonstrations regarding matters such as: the effects of the discharge on other sources and on marine life; standards and procedures for monitoring the discharge; and methods of ensuring control over the sources introducing waste into the POTW. Of this ennead, only the second criterion, embodied in section 1311(h)(2), is relevant to this appeal. 2

To satisfy section 1311(h)(2), a POTW must show that

the discharge of pollutants in accordance with such modified requirements will hot interfere, alone or in combination with pollutants from other sources, with the attainment or maintenance of that water quality which assures protection of public water supplies and the protection and propagation of a balanced, indigenous population of shellfish, fish, and wildlife, and allows recreational activities, in and on the water. ...

33 U.S.C. § 1311(h)(2) (1988). The information necessary for a section 1311(h)(2) demonstration is described by the implementing *603 regulation, under which an applicant who cannot meet the requirements of 40 C.F.R. § 125.61(a)-(e) due to “human perturbations” other than its modified discharge must meet the stressed waters requirements of 40 C.F.R. § 125.61(f). Under these requirements, the applicant must demonstrate that its discharge will not:

(1) contribute to, increase, or perpetuate such stressed conditions;
(2) contribute to further degradation of the biota or water quality if the level of human perturbation from other sources increases; and
(3) retard the recovery of the biota or water quality if the level of human perturbation from other sources decreases.

40 C.F.R. § 125.61(f) (1993). For ease of comprehension, we sometimes will refer to the (f)(1) showing as the “current impacts” showing and the (f)(3) showing as the “future impacts” showing. Although the (f)(2) showing would seem to be intimately related to the (f)(3) showing, it was not discussed in the proceedings below and, therefore, is not a matter of current concern.

Unlike typical NPDES permit proceedings, EPA makes a tentative decision to grant or deny section 1311(h) modifications prior to proposing a permit. See 40 C.F.R. § 125.59(d) (1993). A POTW that has submitted a timely application for such modification may revise it once as of right. See id. § 125.59(d)(1). EPA also may authorize or request the submission of additional information. See id. § 125.59(f)(1).

After issuance of a tentative decision, followed by public notice and opportunity for written comment, EPA makes a final determination in regard to the proposed action. See 40 C.F.R. § 124.15 (1993). That decision becomes the final permit, effective in thirty days, unless it is administratively appealed. See id. § 124.15(b). If an appeal is taken, a party may request an evidentiary hearing to contest the resolution of any question raised in the earlier proceedings. See id. § 124.-74(a). The request must specifically identify the legal and factual issues and their relevance to the permit decision. Id. § 124.-75(a)(1). EPA’s Regional Administrator then grants or denies the request. Id. § 124.-75(a)(1).

If a request for an evidentiary hearing is denied, the denial becomes final agency action within thirty days unless a protest is filed with the Environmental Appeals Board (the Board). See id. §§ 124.60(e)(5), 124.91. In turn, an order by the Board abjuring review renders final the Regional Administrator’s previous decision. See id. § 124.-91(f)(1).

II. PROCEDURAL BACKGROUND

This ease aptly illustrates how the regulatory scheme works. PRASA initially sought a section 1311(h) modification for its Maya-guez sewage facility by application dated September 13, 1979. EPA, hampered by delays in obtaining input from local environmental officials, did not issue a tentative denial of the request until February 6, 1984. One year later, after PRASA presented a revised application, EPA issued another tentative denial. On December 13,1991, following notice, comment, and a two-day public hearing, EPA dashed PRASA’s hopes by issuing a final denial of its request for modification.

Hope, of course, often springs eternal, see Alexander Pope, An Essay on Man, Epistle 1 (1734), and PRASA’s hopes of obtaining a modification were renewed in 1992 by a United States Geological Survey (USGS) report that contained some conclusions helpful to PRASA’s cause. PRASA commenced its administrative appeal of EPA’s final denial by submitting a request for an evidentiary hearing accompanied by the draft USGS study.

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Bluebook (online)
35 F.3d 600, 39 ERC (BNA) 1269, 1994 U.S. App. LEXIS 23913, 1994 WL 462570, Counsel Stack Legal Research, https://law.counselstack.com/opinion/puerto-rico-aqueduct-and-sewer-authority-v-united-states-environmental-ca1-1994.