Last Updated May 24, 2026
Coastal flood risk is often framed as a future consequence of long-term sea-level rise. Yet a deeper and more immediate problem may already be built into the way risk is measured: many coastal hazard models depend on baseline sea-level assumptions that may underestimate the water levels against which coastal land, infrastructure, and communities are exposed.
Sea-level rise is one of the clearest signals of a warming planet, but coastal flood risk is not determined by global mean sea level alone. It depends on the relationship between water and land at specific places: tidal regimes, storm surge, land subsidence, coastal elevation, vertical datums, groundwater withdrawal, sediment compaction, protective infrastructure, wetland loss, and the accuracy of the measurement systems used to connect them. When those baselines are wrong, the map of risk is wrong as well.
This article examines a hidden assumption in coastal climate-risk analysis: the reference level of the sea. Many flood-exposure studies have relied on modeled geoid surfaces or incomplete vertical-reference conversions rather than fully integrating measured coastal sea levels, tide gauges, satellite altimetry, and local elevation data. Recent research suggests that this can lead to systematic underestimation of coastal flood exposure, especially in data-sparse regions, low-lying deltas, small island states, and parts of the Global South.
The issue is not that sea-level-rise science has suddenly been overturned. The deeper lesson is more precise: risk assessment depends on measurement architecture. Climate projections, flood maps, infrastructure designs, insurance models, zoning decisions, port planning, wastewater investments, and adaptation strategies all depend on the quality of the baselines beneath them. When baseline sea level is underestimated, present-day exposure may already be higher than assumed, and future exposure may be underestimated before sea-level rise is even added.
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Why Baselines Matter in Coastal Flood Risk
Coastal flood risk is often described as a problem of rising seas, stronger storms, low-lying land, and vulnerable infrastructure. All of those factors matter. But before a model can estimate which areas will flood, it must answer a more basic question: where is the sea relative to the land?
That question sounds simple, but it is technically demanding. Land elevation is measured relative to vertical reference systems. Sea level varies across geography because of gravity, winds, ocean circulation, tides, temperature, salinity, atmospheric pressure, and coastal geometry. Land itself may be moving because of subsidence, tectonics, sediment compaction, groundwater withdrawal, glacial isostatic adjustment, or construction loads. In a coastal flood model, risk depends on the alignment of all these moving parts.
If the baseline reference level is too low, a model may conclude that a community is higher above the sea than it really is. If coastal elevation data and sea-level data are not referenced consistently, flood exposure may be understated. If local subsidence is ignored, future risk may appear slower-moving than it is. If storm surge, tides, and sea-level rise are modeled without an accurate present-day baseline, adaptation planning can begin from a false sense of safety.
This is why baseline sea level is not merely a technical detail. It is a governance issue. The baseline determines which neighborhoods appear exposed, which infrastructure assets appear vulnerable, which insurance models price risk correctly, which adaptation projects receive priority, and which communities are treated as urgent planning concerns.
When the baseline shifts, the politics of risk shifts with it.
The Hidden Assumption in Coastal Flood Modeling
Many coastal flood models begin with land elevation data and then apply a water-level scenario. The water level may include sea-level rise, tides, storm surge, or compound flooding from rainfall and river discharge. But beneath that process sits a hidden assumption: the modeled reference sea level adequately represents the actual water level along the coast.
Recent research has challenged that assumption. A global review of coastal hazard assessments found that many studies relied on modeled sea-level baselines, especially geoid-based assumptions, rather than direct coastal observations. When modeled baselines were compared with measured coastal sea levels, researchers found that actual present-day coastal sea level may be higher than assumed in many impact assessments, with substantial regional variation.
This does not mean that climate science has been invalidated. Instead, it reveals a problem in the translation layer between climate science, elevation data, hydrodynamic modeling, and risk assessment. The problem is partly geodetic, partly infrastructural, partly institutional, and partly political. Sea-level projections may be scientifically robust, but flood-risk models can still underestimate exposure if the present-day vertical reference frame is misaligned.
The practical implication is stark: some coastal flood-risk assessments may be underestimating risk before future sea-level rise is added.
For planners, this changes the timing of risk. A hazard that appears to belong to 2050 or 2100 may already be closer to present-day exposure conditions. A protective threshold assumed to be adequate may already be less protective. A drainage system designed for historical baselines may already be operating with less margin. A community mapped as marginally safe may already be in a higher-risk category.
Baseline assumptions therefore determine not only what is projected, but what is perceived.
Vertical Datums, Geoids, and Relative Sea Level
To understand why baseline sea level matters, it helps to distinguish three related but different concepts: global mean sea level, modeled reference surfaces, and relative sea level.
Global mean sea level is a planetary-scale indicator. It tracks the average height of the ocean over time, shaped by thermal expansion, glacier melt, ice-sheet mass loss, and changes in terrestrial water storage. It is essential for climate science because it shows how the ocean responds to warming. But coastal flooding does not occur against a global average. It occurs where water reaches land in specific places.
Geoids are modeled gravitational reference surfaces. They approximate what global mean sea level would look like under the influence of Earth’s gravity field if there were no tides, winds, currents, or other dynamic ocean processes. Geoids are indispensable for many geospatial applications, but they are not the same as measured local sea level along every coast.
Relative sea level is the relationship between sea level and land elevation at a particular location. It is the most important concept for coastal flood risk because it includes both ocean change and land movement. If the ocean rises while land remains stable, relative sea level rises. If land subsides while the ocean remains constant, relative sea level also rises. If both occur together, flood risk can accelerate rapidly.
| Concept | What it describes | Why it matters for coastal risk |
|---|---|---|
| Global mean sea level | The average height of the ocean at planetary scale | Tracks climate-driven ocean change but does not determine local flood exposure by itself |
| Geoid | A modeled gravitational reference surface approximating mean sea level | Useful for geodesy and global comparison, but may not match measured coastal water levels in all regions |
| Local mean sea level | Observed or estimated sea level at a specific coast | Provides a more direct baseline for flood modeling when aligned with land elevation data |
| Relative sea level | Sea level relative to land elevation | Determines actual coastal exposure, especially where land subsidence, uplift, or sediment compaction is significant |
| Extreme water level | The combined height of mean sea level, tides, storm surge, waves, and other transient processes | Determines flood events, overtopping risk, infrastructure damage, and emergency exposure |
The key risk emerges when these concepts are mixed without proper conversion. If a study combines land elevation data referenced to one vertical datum with sea-level assumptions referenced to another, the result can misrepresent the relationship between land and water. In low-slope coastal areas, even a modest vertical mismatch can alter the estimated floodplain substantially.
Coastal risk is therefore not just a question of oceanography. It is also a question of geodesy, surveying, remote sensing, data integration, and public infrastructure governance.
Why Small Measurement Errors Can Produce Large Exposure Errors
Coastal flood exposure is highly nonlinear. A small vertical difference in water level can produce a large horizontal expansion of flooded land, especially in flat deltas, coastal plains, estuaries, wetlands, and reclaimed landscapes. The flatter the landscape, the farther floodwater can travel for each additional centimeter of water height.
This is why a baseline error of 20 or 30 centimeters can matter enormously. In a steep rocky coastline, the horizontal change may be limited. In a low-lying delta, the same vertical difference can shift exposure across neighborhoods, roads, ports, farms, industrial zones, wastewater plants, and critical evacuation routes.
Small baseline differences can also change flood frequency. A coastal area that previously flooded during rare storm tides may begin flooding during more common high tides. Drainage systems may back up more frequently. Saltwater may intrude farther inland. Septic systems may fail more often. Roads may become temporarily impassable during ordinary tidal events. Infrastructure designed for occasional flooding may face chronic disruption.
This means baseline uncertainty is not only about the extent of extreme disaster zones. It is also about the transition from rare hazard to recurrent disruption. Coastal risk increases not only when catastrophic floods become larger, but when ordinary water levels begin to interfere with everyday systems.
The nonlinear nature of flood exposure creates three planning challenges:
- Threshold sensitivity: Infrastructure may appear safe until a small change pushes water above a critical elevation.
- Spatial amplification: Small vertical errors can translate into large horizontal exposure changes in low-slope terrain.
- Frequency transformation: Events once considered rare can become frequent as baseline water levels rise.
For coastal planning, uncertainty is not a reason to wait. It is a reason to build greater safety margins into mapping, design, zoning, emergency management, and long-term adaptation pathways.
A Mathematical Lens: Exposure as a Threshold Problem
Coastal flood exposure can be understood as a threshold problem. A location becomes exposed when the relevant water level exceeds the elevation of the land or the protection level of infrastructure.
E_i = \mathbf{1}(H_w + B + S + T + U \geq Z_i + P_i)
\]
Interpretation: A location \(i\) is exposed when water height \(H_w\), baseline correction \(B\), sea-level-rise increment \(S\), tide and surge contribution \(T\), and uncertainty margin \(U\) exceed local land elevation \(Z_i\) plus protective infrastructure height \(P_i\). The indicator \(E_i\) equals 1 when exposure occurs and 0 when it does not.
This simplified equation shows why baseline error matters. If \(B\), the baseline correction, is omitted or underestimated, the model may classify a location as unexposed even when measured coastal water levels place it closer to flood thresholds. The error does not remain isolated inside the model. It affects planning maps, asset exposure estimates, population-risk calculations, benefit-cost analysis, insurance pricing, emergency planning, and infrastructure design.
At the regional scale, total exposed population can be represented as the sum of people living in exposed locations:
P_{exposed} = \sum_{i=1}^{n} Pop_i \cdot E_i
\]
Interpretation: Exposed population is estimated by summing the population \(Pop_i\) of each location classified as exposed. If baseline sea level is underestimated, the exposure indicator \(E_i\) may be too low across many locations, systematically undercounting people at risk.
Infrastructure exposure can be modeled similarly:
A_{risk} = \sum_{j=1}^{m} V_j \cdot \mathbf{1}(H_w + B + S + T + U \geq Z_j + P_j)
\]
Interpretation: Infrastructure risk can be approximated by summing the value or criticality \(V_j\) of assets whose elevation and protection level are exceeded by water levels. The same baseline correction that changes population exposure can also change the apparent vulnerability of ports, wastewater facilities, substations, roads, rail corridors, hospitals, and industrial sites.
These equations are simplified, but they reveal the structural issue. Coastal flood models are not only projections of future water. They are classification systems. They decide which places count as exposed, which assets count as vulnerable, and which communities count as urgent. When the baseline is wrong, the classification is wrong.
Infrastructure Implications
Coastal infrastructure is often built around historical assumptions. Ports, roads, rail lines, airports, seawalls, storm drains, wastewater treatment plants, power stations, refineries, data centers, telecommunications facilities, hospitals, and emergency routes are frequently located near coastlines because coastlines support trade, transportation, settlement, cooling water, drainage, tourism, and industrial access.
Many of these systems were not designed for present-day climate risk, let alone future sea-level rise. They were designed around historical water levels, historical storm records, and local elevation surveys that may not fully reflect present or future conditions. If baseline sea level is higher than assumed, the useful design margin of existing infrastructure may already be smaller than expected.
The consequences differ by system:
| Infrastructure system | Baseline-risk pathway | Potential consequence |
|---|---|---|
| Ports and logistics hubs | Higher baseline water levels increase overtopping, storm-surge reach, and operational disruption | Trade delays, cargo damage, access-road flooding, crane and electrical-system vulnerability |
| Wastewater treatment | Higher sea levels reduce drainage gradients and increase backflow or inundation risk | Service disruption, contamination, public health risk, emergency discharge events |
| Stormwater systems | Outfalls become less effective as receiving waters rise | More frequent urban flooding, compound flooding during rain and high tide, pump dependency |
| Roads and rail | Low-lying corridors face more frequent tidal flooding and storm disruption | Evacuation constraints, supply-chain interruption, maintenance cost escalation |
| Power and energy systems | Coastal substations, plants, fuel storage, and transmission corridors face exposure | Outages, corrosion, cascading infrastructure failures, hazardous-material release |
| Industrial facilities | Floodwater can reach storage tanks, chemical sites, and contaminated land | Environmental contamination, cleanup costs, community exposure, regulatory liability |
| Housing and public facilities | Risk maps may understate exposure for low-lying neighborhoods | Insurance stress, displacement, property-value instability, unequal household losses |
Infrastructure systems are interconnected. A flooded road can prevent workers from reaching a hospital. A failed wastewater system can contaminate floodwater. A damaged substation can interrupt pumping. A port closure can disrupt food, fuel, and medical supply chains. Coastal flood risk therefore becomes a cascading systems problem rather than a single-hazard problem.
Baseline uncertainty makes this harder. If current exposure is underestimated, infrastructure adaptation may be delayed, underfunded, or designed to the wrong standard. Protective systems may appear cost-effective on paper while failing to account for higher actual water levels. Long-lived assets may be approved in places where the real planning horizon is shorter than assumed.
For infrastructure planning, the baseline is destiny. It determines whether systems are built with resilience margins or locked into avoidable vulnerability.
Measurement Systems and Environmental Monitoring
Coastal flood resilience depends on measurement systems. Better adaptation requires not only better climate projections, but better observation of present conditions. This includes tide gauges, satellite altimetry, coastal elevation mapping, land-subsidence monitoring, hydrodynamic models, storm-surge records, wave data, wetland-change mapping, groundwater data, and high-resolution digital elevation models.
Environmental monitoring systems make risk visible. Without them, flood exposure can remain hidden until disaster occurs. With them, planners can detect changing thresholds, update maps, design adaptive infrastructure, prioritize vulnerable communities, and test whether existing defenses remain adequate.
The challenge is integration. Data often sit in separate systems. Tide gauges may be managed by one agency, land elevation by another, flood maps by another, infrastructure inventories by another, and emergency management by another. If the datasets use different reference systems, temporal scales, spatial resolutions, or update cycles, they may fail to support coherent decisions.
A serious coastal monitoring architecture should include:
- High-resolution elevation data for low-lying coastal land, including uncertainty estimates.
- Tide-gauge networks that capture local water-level variation and long-term trends.
- Satellite altimetry for regional and global sea-level monitoring.
- Land-subsidence measurements using GNSS, InSAR, groundwater records, and local surveys.
- Storm-surge and wave modeling that accounts for compound extremes.
- Wetland and shoreline-change monitoring to assess natural protection and erosion.
- Infrastructure exposure inventories for critical assets and lifeline systems.
- Public data portals that make risk evidence transparent and usable.
Measurement is not neutral once it enters governance. What gets measured becomes actionable. What remains unmeasured becomes easier to ignore. Communities without detailed monitoring may be systematically underrepresented in risk assessments, adaptation funding, and emergency planning.
In this sense, coastal data infrastructure is public infrastructure. It determines whether institutions can see the risks they are responsible for managing.
Measurement, Governance, and Climate Risk
The emerging concern about baseline sea-level assumptions highlights a broader governance problem: societies often make long-lived decisions using fragile or incomplete risk baselines. Zoning, permitting, insurance, infrastructure investment, port expansion, coastal housing, industrial siting, and adaptation finance all depend on models. But models are only as trustworthy as the assumptions, data, and institutional processes behind them.
Coastal flood governance must therefore treat baseline uncertainty as a risk multiplier. A flood map should not be interpreted as a fixed boundary between safe and unsafe land. It should be interpreted as a decision tool shaped by data quality, model assumptions, vertical datums, update cycles, uncertainty ranges, and social priorities.
Several governance principles follow:
- Use measured local baselines wherever possible. Coastal flood assessments should integrate tide-gauge records, satellite observations, and local elevation data rather than relying on generalized reference surfaces alone.
- Make uncertainty visible. Maps should show confidence ranges, vertical error, datum assumptions, and exposure sensitivity.
- Update risk maps regularly. Static flood maps become obsolete as sea level, land subsidence, development, wetlands, and infrastructure conditions change.
- Apply precaution to long-lived assets. Infrastructure expected to last 50 to 100 years should not be designed around narrow baseline assumptions.
- Prioritize critical lifelines. Hospitals, evacuation routes, substations, wastewater systems, ports, and emergency services require higher resilience margins.
- Protect public accountability. Technical modeling choices should be documented clearly enough for public review, legal scrutiny, and institutional learning.
Climate governance is often described as a challenge of emissions reduction and adaptation finance. It is also a challenge of measurement integrity. If the baseline is wrong, the adaptation strategy may be misdirected. If uncertainty is hidden, public choices become less accountable. If vulnerable communities are unmapped, they become easier to neglect.
Good measurement does not eliminate political conflict. But it improves the quality of the conflict by making trade-offs clearer, assumptions visible, and institutional responsibility harder to evade.
Planetary Boundaries and Coastal Exposure
Coastal flood risk also belongs within the wider planetary-boundaries conversation. Sea-level rise is driven by climate change, but its impacts interact with multiple Earth-system pressures: land-system change, freshwater disruption, biosphere degradation, ocean warming, pollution, and the loss of natural coastal buffers.
Coasts are boundary zones in both the physical and institutional sense. They connect land, ocean, atmosphere, rivers, wetlands, cities, ports, and global trade. When planetary systems destabilize, coasts often register the combined effects. A coastal flood is not only water crossing a shoreline. It can be the convergence of ocean warming, ice melt, land subsidence, wetland loss, urban expansion, infrastructure exposure, and unequal development.
This makes coastal flood risk a useful example of how planetary boundaries become local governance problems. The climate system may be planetary, but the consequences appear in specific neighborhoods, deltas, islands, ports, roads, and public budgets. The ocean may rise globally, but the harm is mediated by local elevation, land-use decisions, building codes, drainage systems, protective ecosystems, insurance markets, and political power.
Planetary-boundaries thinking also helps prevent a narrow engineering response. Seawalls, levees, pumps, and barriers can be necessary, but they are not sufficient by themselves. Coastal resilience may also require wetland restoration, managed retreat, land-use reform, groundwater governance, sediment management, emissions reduction, ecosystem protection, and more honest accounting of long-term exposure.
The baseline problem reinforces this lesson. If present risk is underestimated, adaptation may appear less urgent than it is. If future sea-level rise is layered onto an underestimated present-day baseline, the whole trajectory of exposure may be shifted downward. This can produce adaptation deficits that are not only financial, but epistemic: societies fail to act because their systems for seeing risk are incomplete.
Planetary limits become dangerous when institutions translate them into weak baselines, delayed warnings, and underbuilt defenses.
Equity, Global Exposure, and Unequal Baseline Risk
Coastal flood exposure is not distributed evenly. Some of the world’s most vulnerable coastal communities are located in deltas, small islands, informal settlements, low-elevation urban districts, reclaimed coastal land, and regions where monitoring infrastructure is limited. These are often places where baseline errors can have the most serious consequences.
Data gaps are not merely technical gaps. They can become justice gaps. Regions with dense tide-gauge networks, high-resolution elevation data, strong surveying institutions, and well-funded adaptation agencies are better positioned to detect and correct baseline problems. Regions without those resources may have risk underestimated precisely where vulnerability is greatest.
This matters for the Global South, small island developing states, coastal megacities, and delta regions where large populations live near sea level. A modest vertical underestimation can affect millions of people when settlements are dense and terrain is flat. It can alter estimates of exposure, relocation need, infrastructure cost, adaptation finance, and loss-and-damage claims.
Equity also matters within wealthy countries. Coastal risk often follows existing lines of inequality. Lower-income households may live in more exposed areas, have fewer resources for elevation or relocation, face higher insurance burdens, and depend more heavily on public infrastructure. Historically marginalized communities may face toxic flood exposure near industrial sites, ports, refineries, landfills, or contaminated land.
Accurate baselines are therefore part of climate justice. They help determine whose risk is counted, whose infrastructure is protected, whose property is insurable, whose losses are anticipated, and whose future is considered worthy of investment.
A responsible coastal-risk framework should ask:
- Which communities are missing from high-resolution exposure mapping?
- Where are vertical-datum uncertainties largest?
- Which regions lack tide gauges, subsidence monitoring, or updated elevation data?
- Which infrastructure systems serve vulnerable populations?
- How do baseline assumptions affect adaptation funding priorities?
- Who has the authority to challenge or revise official risk maps?
Risk that is not measured is often risk that is transferred to those with the least power to contest it.
Planning Implications for Coastal Adaptation
For policymakers, planners, engineers, insurers, and public agencies, uncertainty in baseline sea level should change the planning posture. It should not produce paralysis. It should produce more careful design margins, more frequent map updates, and more adaptive decision-making.
Coastal infrastructure often operates on long time horizons. A bridge, wastewater treatment plant, port terminal, stormwater tunnel, hospital, highway, or energy facility may be expected to function for decades. If design standards rely on underestimated present-day sea level, the asset may enter service already closer to failure thresholds than intended.
Planning should therefore shift from static protection to adaptive pathways. Instead of asking only whether an asset survives one projected scenario, institutions should ask how decisions can adjust as observations improve and thresholds are approached.
| Planning task | Conventional approach | Stronger baseline-aware approach |
|---|---|---|
| Flood mapping | Use static floodplain boundaries | Update maps with measured sea level, datum corrections, subsidence, uncertainty bands, and local observations |
| Infrastructure design | Design to a fixed return period or historical baseline | Design with adaptive margins, observed baseline corrections, future sea-level scenarios, and failure-threshold analysis |
| Land-use planning | Permit development based on current official maps | Apply precaution where baseline uncertainty, subsidence, or low-slope exposure could shift risk rapidly |
| Insurance and finance | Price risk from existing exposure models | Incorporate baseline uncertainty, recurrent flooding, asset lifetime, and map-update risk |
| Emergency management | Plan for mapped flood zones | Stress-test evacuation routes, hospitals, utilities, and shelters under higher baseline assumptions |
| Adaptation funding | Prioritize projects based on modeled exposure | Correct for data gaps and ensure vulnerable communities are not undercounted because monitoring is weak |
Baseline-aware adaptation also means distinguishing between reversible and irreversible choices. Temporary measures, zoning restrictions, monitoring upgrades, and modular defenses can be adjusted over time. Large infrastructure investments, coastal development approvals, land reclamation, and relocation decisions can lock in vulnerability or resilience for generations.
The central planning principle is simple: do not treat uncertain baselines as safe baselines. Where uncertainty is large and consequences are severe, planning should err toward resilience, transparency, and flexibility.
GitHub Repository
The companion repository for this article can support reproducible coastal flood-risk workflows, baseline-sensitivity analysis, synthetic exposure modeling, infrastructure-threshold testing, and transparent documentation of how sea-level assumptions affect risk estimates.
Complete Code Repository
This repository provides a companion technical workspace for coastal flood-risk analysis, including synthetic data, baseline sea-level sensitivity checks, elevation-threshold modeling, infrastructure exposure tables, and reproducible Python, R, SQL, and systems-code examples for examining how measurement assumptions affect climate-risk assessment.
The Broader Lesson for Infrastructure Planning
Climate risk is often framed as a future problem: seas will rise, storms will intensify, infrastructure will need to adapt. That framing is partly true, but it can obscure a more immediate issue. Present risk may already be mismeasured.
The baseline problem shows how deeply climate risk depends on the systems used to observe it. A flood map is not just a map. It is a chain of assumptions about vertical datums, land elevation, sea level, tidal behavior, storm dynamics, protective infrastructure, exposure thresholds, and acceptable uncertainty. If that chain contains weak links, public decisions inherit the weakness.
Coastal resilience therefore requires more than stronger walls and higher roads. It requires better measurement systems, clearer uncertainty communication, transparent model assumptions, stronger environmental monitoring, accountable planning institutions, and a willingness to revise risk categories as evidence improves.
Sea-level rise is not only a story about melting ice sheets and warming oceans. It is also a story about measurement, modeling, infrastructure, governance, and the translation of science into public responsibility. When baseline measurements change, the map of risk changes as well.
And when the map of risk changes, so should the decisions built upon it.
Related articles
- Risk & Resilience
- Planetary Boundaries
- Environmental Monitoring Systems
- Intelligent Infrastructure Systems
Further reading
- IPCC. Climate Change 2021: The Physical Science Basis.
- IPCC. Special Report on the Ocean and Cryosphere in a Changing Climate, Chapter 4: Sea Level Rise and Implications for Low-Lying Islands, Coasts and Communities.
- NASA Sea Level Change Portal.
- NOAA Sea Level Rise Viewer.
- U.S. Sea Level Rise Technical Report.
- World Bank. Disaster Risk Management and Climate Resilience Resources.
References
- Hamlington, B.D. et al. (2024). The rate of global sea level rise doubled during the past three decades. Communications Earth & Environment.
- IPCC. (2021). Climate Change 2021: The Physical Science Basis. Working Group I Contribution to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change.
- IPCC. (2019). Chapter 4: Sea Level Rise and Implications for Low-Lying Islands, Coasts and Communities. Special Report on the Ocean and Cryosphere in a Changing Climate.
- NASA. Sea Level Change Portal.
- NOAA Office for Coastal Management. Sea Level Rise Viewer.
- Seeger, K. and Minderhoud, P.S.J. et al. (2026). Sea level much higher than assumed in most coastal hazard assessments. Nature.
- Sweet, W.V. et al. (2022). Global and Regional Sea Level Rise Scenarios for the United States: Updated Mean Projections and Extreme Water Level Probabilities Along U.S. Coastlines. National Oceanic and Atmospheric Administration.
