Preserve Responsible Shoreline, V. City Of Bainbridge Island

CourtCourt of Appeals of Washington
DecidedDecember 13, 2022
Docket56808-0
StatusUnpublished

This text of Preserve Responsible Shoreline, V. City Of Bainbridge Island (Preserve Responsible Shoreline, V. City Of Bainbridge Island) is published on Counsel Stack Legal Research, covering Court of Appeals of Washington primary law. Counsel Stack provides free access to over 12 million legal documents including statutes, case law, regulations, and constitutions.

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Preserve Responsible Shoreline, V. City Of Bainbridge Island, (Wash. Ct. App. 2022).

Opinion

Filed Washington State Court of Appeals Division Two

December 13, 2022 IN THE COURT OF APPEALS OF THE STATE OF WASHINGTON

DIVISION II PRESERVE RESPONSIBLE SHORELINE MANAGEMENT, Alice Tawresey, Robert Day, No. 56808-0-II Bainbridge Shoreline Homeowners, Dick Haugan, Linda Young, Don Flora, John Rosling, Bainbridge Defense Fund, Gary Tripp, and Point Monroe Lagoon Home Owners Association, Inc.,

Appellants,

v. UNPUBLISHED OPINION

CITY OF BAINBRIDGE ISLAND, Washington State Department of Ecology, Environmental Land Use Hearing Office and Growth Management Hearings Board Central Puget Sound Region,

Respondents,

and

Kitsap County Association of Realtors,

Intervenor Below.

PRICE, J. — Preserve Responsible Shoreline Management (PRSM) appeals the Growth

Management Hearing Board’s (Board) order upholding the City of Bainbridge Island’s (City)

shoreline master program (Master Program). PRSM asserts the following grounds for relief under

the Administrative Procedure Act (APA):1 the Board erroneously interpreted or applied the law,

1 Ch. 34.05 RCW. No. 56808-0-II

the Board’s order was not supported by substantial evidence, and the Board’s order was arbitrary

or capricious. PRSM also asserts that the Master Program was unconstitutional. We determine

that PRSM fails to meet its burden for relief and affirm.

FACTS

I. BAINBRIDGE ISLAND MASTER PROGRAM UPDATE

In 2010, the City began updating its Master Program. The City commissioned several

scientific studies to help determine how to protect the shoreline and received public comments on

the update to the Master Program.

A. SCIENTIFIC STUDIES

One study, commissioned by the City in 2003, was the Bainbridge Island Nearshore

Assessment. The study summarized the then-available science applicable to the shorelines in

Bainbridge Island. The study discussed various aspects of the shoreline ecosystem, including

discussion of nearshore animal species, nearshore habitats and ecological functions, nearshore

physical processes such as erosion and tides, and impacts of human shoreline modifications like

bulkheads on nearshore habitats. The study made several recommendations, including that the

City produce an inventory of the Bainbridge Island shoreline where the marine habitats meet land.

The second study, commissioned by the City in 2004, was the Bainbridge Island Nearshore

Habitat Characterization & Assessment, Management Strategy Prioritization, and Monitoring

Recommendations (Nearshore Habitat Characterization). The study separated the 53 miles of

shoreline into 9 management areas, comprised of 201 individual shoreline reaches. Each shoreline

reach was given an individual ecological function score based in its geomorphology, habitat

structure, habitat processes, and other controlling factors.

2 No. 56808-0-II

In 2010, the City commissioned Coastal Geologic Services Inc. to prepare the Bainbridge

Island Current and Historic Coastal Geomorphic/Feeder Bluff Mapping. The purpose of the study

was to “to map coastal geomorphic shoretypes (such as ‘feeder bluffs’) and prioritize restoration

and conservation sites along the marine shores of Bainbridge Island nearshore . . . .”

Administrative Record (AR) at 4152. The study divided the shoreline into 32 areas called “drift

cells” and assessed their ability to serve as “functioning sediment sources and transport pathways”

necessary to maintain intact coastal geomorphic processes. AR at 4153, 4160. The study

addressed the negative impacts of shoreline modifications, such as bulkheads and other forms of

shore armoring. The study stated that “sediment impoundment is probably the most significant

negative impact” of shore armoring, that “[s]everal habitats of particular value to the nearshore

ecosystem rely on intact geomorphic processes and are commonly impacted by shore armor,” and

that shoreline armoring “can have substantial negative impacts on nearshore habitats” through the

loss of marine vegetation, the loss of nearshore large woody debris, and the “partial or major loss

of spits that form estuaries and embayments.” AR at 4154-55.

In 2011, the City also commissioned an update to the 2003 and 2004 studies, the Addendum

to the Summary of the Science Report (Addendum) by Herrera Environmental Consultants Inc.

(Herrera). The Addendum relied on more than 250 sources, including studies and reports specific

to the Puget Sound. The purpose of the Addendum was to provide “updated information on

shoreline and nearshore ecology, physical processes, habitats, and biological resources of

Bainbridge Island” and make recommendations for implementation of the “no net loss” standard

and for “marine shoreline protective buffers considering geomorphic conditions and shoreline

vegetation.” AR at 4240-41. Specific to the buffers, the Addendum stated that “[b]uffers can be

3 No. 56808-0-II

important to the protection of the functions and processes of the nearshore environments along

marine coastlines,” and suggested different approaches to shoreline buffers. AR at 4306. The two

suggestions for shoreline buffers included fixed-width buffers based on typical conditions present

on Bainbridge Island and variable-width buffers, which could result from the different site

conditions and resources to be protected. The Addendum stated:

Approaches to establishing buffers vary between fixed or variable width, with the former generally being the most common (Haberstock et al. 2000). To be effective under a worst-case scenario, and to ensure success in the face of uncertainty about specific site conditions, May (2000) and Haberstock (2000) suggest that fixed- width buffers should be designed conservatively (i.e., larger than the bare minimum needed for protection).

AR at 4314.

Based on the Addendum, the City requested that Herrera make specific recommendations

for shoreline buffers to be incorporated into the Master Program. Herrera created two memoranda:

August 11, 2011, Memorandum re: Documentation of Marine Shoreline Buffer Recommendation

Discussions and August 31, 2011, Memorandum re: Clarification on Herrera August 11, 2011,

Documentation of Marine Shoreline Buffer Recommendation Discussions Memo. The

memoranda explained that shoreline buffers protect a wide variety of ecological functions,

including water quality and mineralization, fine sediment control, shade/microclimate, fish and

invertebrate food from litterfall and large woody debris, and hydrology/slope stability. The

memoranda summarized the buffer width recommendations made throughout relevant scientific

literature and how the buffer widths widely vary based on the protection goal of the buffer. Buffer

4 No. 56808-0-II

width recommendations mostly ranged from 16 to 328 feet, with the buffers width

recommendation for removing pollution from stormwater runoff reaching 1,969 feet. The buffers

in the scientific research were what the literature stated was necessary to achieve at least 80 percent

buffer effectivity.

Herrera recommended that the City establish a two-tiered buffer system. Herrera

recommended that “Zone 1” be established as a “riparian protection zone” in which existing native

vegetation would be preserved and development would be significantly restricted. AR at 4362.

This recommendation was based on the ecological functions provided by native vegetation close

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