Strafach v. Durfee

635 A.2d 277, 1993 R.I. LEXIS 277, 1993 WL 533787
CourtSupreme Court of Rhode Island
DecidedDecember 23, 1993
Docket92-531-M.P.
StatusPublished
Cited by19 cases

This text of 635 A.2d 277 (Strafach v. Durfee) is published on Counsel Stack Legal Research, covering Supreme Court of Rhode Island primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

Bluebook
Strafach v. Durfee, 635 A.2d 277, 1993 R.I. LEXIS 277, 1993 WL 533787 (R.I. 1993).

Opinion

OPINION

SHEA, Justice.

This case came before the Supreme Court pursuant to the petition for certiorari of Louise Durfee, the defendant director of the Rhode Island Department of Environmental Management (DEM), to review a decision of the Superior Court that reversed DEM’s de *278 nial of variances sought by the plaintiffs, John and Loretta Strafach (the Strafachs). We quash the judgment of the Superior Court.

The Strafachs are the owners of real property located in the town of Westerly described as lot Nos. 279, 280, and 281 on tax assessor’s plat No. 165 (the property). The property is located on both the north and the south sides of Atlantic Avenue in the Mis-quamicut section of Westerly. The parcel on the north side of Atlantic Avenue is adjacent to Winnapaug Pond. A motel and efficiency units were located on that side of the property. The parcel on the south side is adjacent to the Atlantic Ocean. On that side of the property there were two restaurants, a bar, a parking lot, and several motel units.

In October of 1989 the Strafachs sought to destroy the existing structures on the ocean side of the property and to replace them with a cabana complex composed of 200 cabana units, a restaurant and bar, and several townhouse units. As part of this proposed plan, the Strafachs intended to replace the existing multiple cesspool configuration with an individual sewage disposal system (ISDS) located on the ocean side of the property which facility would service the entire development.

Pursuant to G.L.1956 (1993 Reenactment) chapter 17.1 of title 42, G.L.1956 (1991 Reenactment) chapter 12 of title 46, and G.L.1956 (1987 Reenactment) chapter 56 of title 5, the director of DEM and the Environmental Standards Board have been delegated the authority to promulgate, administer, and enforce rules and regulations regarding (ISDS). The director is required “to issue and enforce such rules, regulations, and orders as may be necessary to carry out the duties assigned to the director and the Department by any provision of law.” Section 42-17.1-2(s). In addition, the director is specifically directed to “establish minimum standards, subject to the approval of the environmental standards board, relating to the location, design, construction, and maintenance of all sewage disposal systems.” Section 42-17.1-2(0-These minimum standards are set forth in SD Rules and Regulations Establishing Minimum Standards Relating To Location, Design, Construction, And Maintenance Of Individual Sewage Disposal Systems (hereinafter ISDS Regulations) are properly promulgated minimum standards under the authority of § 42-17.1-2(1), (m), (r), and (s).

The Strafachs included a copy of the 1980 amended version of the ISDS Regulations in the appendix to their brief and made reference to the 1980 rule numbers throughout their brief. Both the variance request form submitted by the Strafachs and DEM’s own memo of April 16,1990, denying the variance request, cite the 1980 amended version of the rules. The DEM, however, supplied the 1992 amended version of the ISDS Regulations and referenced the 1992 rule numbers in its brief. We note that the 1990 version of the ISDS Regulations-, promulgated in December 1989 and effective January 2, 1990, should have been applied to the variance request in this case. ISDS Regulation SD 22.02(1) of the 1990 version provides that “a request for a variance pursuant to SD 20.01 may be filed with the director where an application was filed with the director on or before the effective date of these rules [January 2, 1990] [and] no action has been taken by the director denying or approving such application.” This is precisely the factual scenario of the present case. The different versions of the rules do not differ substantively, however. Since both parties initially cited and relied upon the 1980 version of the rules, we will refer to those rule numbers in this opinion.

The Strafachs submitted an application to DEM’s Division of Groundwater and Freshwater Wetlands requesting permission to construct the new ISDS in October of 1989. In January of 1990, while the October 1989 application was still pending and no action had been taken by DEM, the Strafachs submitted a request for three variances from the ISDS Regulations. 1 The first variance, *279 which is the main focus of this case, relates to ISDS Regulation SD 3.05(e). This regulation specifies the minimum distance required between an ISDS and a coastal erosion-prone site. In order to understand the nature of this regulation, it is necessary to have a basic understanding of the Coastal Resources Management Council (CRMC).

The CRMC was established by the Legislature to regulate the use of land located near coastal waters. G.L.1956 (1991 Reenactment) chapter 23 of title 46. The CRMC was deemed to be the “principal mechanism for management of the state’s coastal resources.” Section 46-23-l(c). This legislative delegation of authority lies within the permissible bounds of article 6 of the Rhode Island Constitution. Milardo v. Coastal Resources Management Council, 434 A.2d 266 (R.I.1981). As we noted in Santini v. Lyons, 448 A.2d 124 (R.I.1982), the Legislature, being mindful of the importance and use of the coastal environment and recognizing the damage already done, could rationally conclude that it was necessary to single out coastal areas for specific regulation.

In meeting these objectives, the CRMC has been given the authority to develop policies, programs, and regulations that pertain to coastal areas. Section 46-23-6. The CRMC program has designated certain coastal regions as “erosion-prone.” Both parties have acknowledged that the proposed site for the ISDS in this new development has been designated as such an area. ISDS Regulation SD 3.05(e) pertains to the construction of ISDS on erosion-prone areas. This regulation states in part:

“Where an individual sewage disposal system will be located in the proximity of the active ocean on sites subject to erosion caused by coastal storm * ⅜ ⅜ the minimum setback requirement from the spring (moon) tide elevation to the edge of the system shall not be less than 150 feet.” ISDS Regulation SD 3.05(e).

In simple terms the regulation prohibits the construction of any ISDS within 150 feet of the ocean in such designated erosion-prone areas. The proposed system would be only 115 feet from the elevation, thus requiring a 35-foot variance. In addition both parties acknowledge that there was a definite “scarp” on the site located approximately 60 to 65 feet inland from the moon high-tide line.

A scarp was consistently described in the testimony as a steep slope created by the erosive forces of wind and wave action. The sand is dug out by wave action during the winter months and deposited offshore in a sandbar. In the late spring and early summer the sand is redeposited on the beach, and the scarp disappears. Essentially a scarp is a seasonal short-term erosion. Providing that no long-term beach erosion occurs at a particular site, the scarp should reappear in the same area year after year.

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Bluebook (online)
635 A.2d 277, 1993 R.I. LEXIS 277, 1993 WL 533787, Counsel Stack Legal Research, https://law.counselstack.com/opinion/strafach-v-durfee-ri-1993.