In the coastal context, a setback is generally the required distance a structure must be located behind a baseline, like a tidal line (e.g., mean high or low water) or various types of natural features (e.g., a coastal dune, wetland, or floodplain).See footnote 1 Setbacks are typically designed to keep development away from portions of a property that are subject to coastal threats like flooding or erosion.See footnote 2
Setbacks are often specific to or tailored for individual properties whereby governments apply any combination of three common factors, as specified in the relevant law or regulations: (1) the size or square footage of a proposed development or structure; (2) the location of a baseline relative to the proposed development or structure; and (3) the level and severity of the physical risk facing that structure over a given time period (e.g., the lifespan of a structure). Nonetheless, governments can also implement standard setback distances for every property to which the requirement applies.
Similar to setbacks, buffers or buffer zones require landowners to leave parts of their property undeveloped to preserve them and their important natural functions.See footnote 3 Governments commonly use buffers to prohibit property owners from building structures on or immediately adjacent to wetlands and coastal dunes.See footnote 4
Setback and buffer requirements vary and are usually implemented via state and local coastal, environmental, and natural resources laws and regulations and local land-use and floodplain ordinances.
With setbacks and buffers, state and local governments can require property owners seeking a development (or redevelopment) permit to site structures and infrastructure away from vulnerable coastal areas, while simultaneously conserving important habitats and natural resources. Most setbacks and buffers will cover areas and be designed in ways that serve a dual or reciprocal benefit to protect people and the structures behind it, in addition to protecting the natural features they are conserving; however, the purpose and ecosystem benefits of some setbacks and buffers may be different based on location or type of physical risk. For example, setbacks and buffers could be used to site development away from highly erosive shorelines or intertidal areas that will be lost in the future and/or higher ground or adjacent tidal areas that can facilitate inland wetland migration.
To support managed retreat efforts, setbacks and buffer distances can factor in future sea-level rise and erosion rates, but to do so requires significant investment in data collection and science to determine the rates that will be used to best achieve regulatory objectives. Governments may also have to evaluate and amend setback and buffer requirements, including what serves as the baseline, as physical conditions change over time (e.g., the rate of sea-level rise or erosion accelerates). For example, governments could consider setting fixed or permanent baselines for setbacks and buffers — for which no future development could occur seaward of that baseline — or move a baseline landward, as desired in response to local needs or concerns. From an administrative perspective, periodic updates to baselines can require lengthy and staff intensive regulatory processes. In comparison, dynamic baselines that, by law, are allowed to migrate landward (or seaward) with shifting coastlines and would not require a statutory or regulatory change can create more flexibility for agencies and potentially serve as a more effective climate adaptation strategy.
Setbacks and buffers allow governments to facilitate managed retreat in a way that can enable people to stay on their properties longer. These tools are likely to be more feasible and a regulatory option in rural areas or communities with more land and larger lot sizes where setbacks and buffers can be implemented without preventing all development on a given parcel.
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The primary legal considerations concerning setbacks and buffers will relate to constitutional takings and environmental and natural resources statutes and regulations at the state and local levels.
Jurisdictions can design setbacks and buffers to withstand potential regulatory takings challenges. The Fifth Amendment of the U.S. Constitution and analogous provisions of state constitutions prohibit governments from “taking” private property without just compensation.See footnote 5 While there are different types of takings, courts apply a “per se” test to physical occupationsSee footnote 6 and regulations that deprive a private property owner of all or essentially all of his/her property’s economic value;See footnote 7 however, in a managed retreat context, most setback and buffer regulations designed to protect people, property, and the coastal environment will be evaluated under a case-by-case-specific balancing test.See footnote 8 Generally, governments can use setbacks and buffers to restrict or limit development in vulnerable coastal areas and floodplains, so long as a property maintains some economic value and a regulation serves a legitimate public interest, such as safety or to offset ecological impacts resulting from use of private property.
Governments can avoid or mitigate potential takings risks by ensuring that setback and buffer requirements are informed by science and plans. At a minimum, governments should: clearly justify the need for setbacks and buffers based on best available science; articulate the purpose for these requirements in planning and other documents that put affected private property owners on sufficient notice; and design and implement them on a spatial scale that is proportionate to the coastal hazard being mitigated. For more information on takings and recommendations to minimize legal risk, see the Crosscutting Legal Considerations>Takings section of this toolkit.
In addition to takings, governments should also evaluate how setbacks and buffers may intersect with other environmental and natural resources laws and regulations, particularly under the federal Clean Water ActSee footnote 9 and complementary state and local laws that protect wetlands and open space areas. By comprehensively viewing these types of laws in a managed retreat context, policymakers can avoid potential conflicts between laws and agencies by assessing where there are synergies to promote coastal conservation in a changing climate.
When implementing setbacks and buffers in a managed retreat context, decisionmakers may consider the following practice tips to address and balance different legal and policy tradeoffs:
Endnotes:
1. Jessica Grannis, Georgetown Climate Ctr., Adaptation Toolkit: Sea-Level Rise and Coastal Land Use 26 (Oct. 2011), available at View Source; Black’s Law Dictionary (11th ed. 2019) (Generally, a setback is “The minimum amount of space required between a lot line and a building line. Typically contained in zoning ordinances or deed restrictions, setbacks are designed to ensure that enough light and ventilation reach the property and to keep buildings from being erected too close to property lines.”). | Back to contentBack to content
2. Jessica Grannis, Georgetown Climate Ctr., Adaptation Toolkit: Sea-Level Rise and Coastal Land Use 26 (Oct. 2011), available at View Source. | Back to contentBack to content
5. U.S. Const. amend. V. Back to contentBack to content
6. J. Peter Byrne & Jessica Grannis, Chapter Nine: Coastal Retreat Measures, in The Law of Adaptation to Climate Change: U.S. and International Aspects 274–75 (Michael B. Gerrard & Katrina Fischer Kuh eds., 2012). Back to contentBack to content
7. Lucas v. S.C. Coastal Council, 505 U.S. 1003 (1992); J. Peter Byrne & Jessica Grannis, Chapter Nine: Coastal Retreat Measures, in The Law of Adaptation to Climate Change: U.S. and International Aspects 275–76 (Michael B. Gerrard & Katrina Fischer Kuh eds., 2012). Back to contentBack to content
8. Penn. Cent. Transp. Co. v. City of New York, 438 U.S. 104 (1978); J. Peter Byrne & Jessica Grannis, Chapter Nine: Coastal Retreat Measures, in The Law of Adaptation to Climate Change: U.S. and International Aspects 276–77 (Michael B. Gerrard & Katrina Fischer Kuh eds., 2012). Back to contentBack to content
9. Clean Water Act, 33 U.S.C. §§ 1251 et seq. (2020). Back to contentBack to content
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