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#2 OPSD Cumulative Impact Guidance
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#2 OPSD Cumulative Impact Guidance
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4. Spatial and temporal parameters to scope past, present and future actions in SMA <br />permitting <br />In accordance with the definition of "cumulative impact " previously defined in CEQ's rule <br />or in HAR Chapter I 1-200.1, and the research on the Final EAs/EISs available from Office <br />of Environmental Quality Contro14 (OEQC) online library, spatial and temporal boundaries <br />are two critical parameters to scope past, present, and reasonably foreseeable future actions <br />that need to be taken into account in cumulative impact assessments. Principally, spatial <br />and temporal scopes for assessments depend on the scale of a proposed action, and on <br />target resources and/or environment. Each affected resource, ecosystem, and human <br />community should be analyzed in terms of its capacity to accommodate additional effects, <br />based on its own time and space parameters. Ideally, spatial and temporal scopes for <br />cumulative effect/impact assessments should be expanded to the point at which a specific <br />coastal resource is no longer significantly affected, or the impacts are no longer of interest <br />to affected parties. However, categorizing and determining the geographic and temporal <br />scope of cumulative effects/impacts in the SMA permitting process can significantly divert <br />the county planning departments from focusing their time and resources on the most <br />significant effects. Given that existing cumulative effects/impacts analysis guidance from <br />CEQ and HEPA is not provided in the context of the SMA, there remains ambiguity in its <br />application and implementation. This SMA-oriented guidance seeks to narrow down the <br />spatial and temporal scopes of the cumulative effect/impact assessments. <br />With respect to spatial scope, setting the consideration at an existing defined boundary <br />such as the SMA boundary within the county jurisdiction would reduce uncertainty in <br />assessing an appropriate scope. The SMAs designated by the counties generally begin at <br />the shoreline and extend to the nearest highway or several miles inland. Other factors, <br />such as salinity and tidal influences on bodies of surface water, also affect a SMA <br />boundary. Pursuant to HRS §205A-23, as amended, the SMA in each county shall be as <br />shown on such maps filed with the county authority as of June 8, 1977. To narrow down <br />the scoping to a meaningful assessment and include what counts for cumulative <br />effect/impact assessments in SMA permitting, it would be appropriate and feasible to apply <br />the SMA boundary as a spatial parameter if no critical issues on coastal resources or <br />environment are raised beyond the SMA. The OPSD recommends a geographic radius up <br />to the SMA inland boundary from the shoreline as the minimum spatial scope to assess the <br />incremental impacts of a proposed action on the SMA when added to other past, present, <br />and reasonably foreseeable future actions. <br />Besides geographic scope, temporal scale is another crucial parameter to scope past and <br />future actions to assess cumulative effects/impacts resulting from a proposed action. <br />"Reasonably foreseeable" actions are those that are likely to occur, rather than those that <br />are merely possible or subject to speculation. Reasonably foreseeable future actions are <br />those that have the potential to overlap spatially or temporally with a proposed project. It <br />is recognized that a SMA Use Permit is usually granted to complete a proposed <br />4 The Office of Environmental Quality Control has been renamed as `Environmental Review Program" <br />within the OPSD, enacted by Act 152, SLH 2021. <br />
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