Skip to main content
Proceedings of the National Academy of Sciences of the United States of America logoLink to Proceedings of the National Academy of Sciences of the United States of America
. 2015 Oct 12;112(44):13508–13513. doi: 10.1073/pnas.1511186112

Carbon choices determine US cities committed to futures below sea level

Benjamin H Strauss a,1, Scott Kulp a, Anders Levermann b,c
PMCID: PMC4640796  PMID: 26460051

Significance

As greenhouse gas emissions continue to rise, the window to limit global warming below 2 °C appears to be closing. Associated projections for sea-level rise generally range near or below 1 m by 2100. However, paleontological and modeling evidence indicates long-term sea-level sensitivity to warming that is roughly an order of magnitude higher. Here we develop relationships between cumulative carbon emissions and long-term sea-level commitment and explore implications for the future of coastal developments in the United States. The results offer a new way to compare different emissions scenarios or policies and suggest that the long-term viability of hundreds of coastal municipalities and land currently inhabited by tens of millions of persons hang in the balance.

Keywords: climate change, climate impacts, sea-level rise

Abstract

Anthropogenic carbon emissions lock in long-term sea-level rise that greatly exceeds projections for this century, posing profound challenges for coastal development and cultural legacies. Analysis based on previously published relationships linking emissions to warming and warming to rise indicates that unabated carbon emissions up to the year 2100 would commit an eventual global sea-level rise of 4.3–9.9 m. Based on detailed topographic and population data, local high tide lines, and regional long-term sea-level commitment for different carbon emissions and ice sheet stability scenarios, we compute the current population living on endangered land at municipal, state, and national levels within the United States. For unabated climate change, we find that land that is home to more than 20 million people is implicated and is widely distributed among different states and coasts. The total area includes 1,185–1,825 municipalities where land that is home to more than half of the current population would be affected, among them at least 21 cities exceeding 100,000 residents. Under aggressive carbon cuts, more than half of these municipalities would avoid this commitment if the West Antarctic Ice Sheet remains stable. Similarly, more than half of the US population-weighted area under threat could be spared. We provide lists of implicated cities and state populations for different emissions scenarios and with and without a certain collapse of the West Antarctic Ice Sheet. Although past anthropogenic emissions already have caused sea-level commitment that will force coastal cities to adapt, future emissions will determine which areas we can continue to occupy or may have to abandon.


Most studies on the projected impacts of anthropogenic climate change have focused on the 21st century (1). However, substantial research indicates that contemporary carbon emissions, even if stopped abruptly, will sustain or nearly sustain near-term temperature increases for millennia because of the long residence time of carbon dioxide in the atmosphere and inertia in the climate system, e.g., the slow exchange of heat between ocean and atmosphere (25). Earth system and carbon-cycle feedbacks such as the release of carbon from thawing permafrost or vegetation changes affecting terrestrial carbon storage or albedo may further extend and possibly amplify warming (6).

Paleontological records indicate that global mean sea level is highly sensitive to temperature (7) and that ice sheets, the most important contributors to large-magnitude sea-level change, can respond to warming on century time scales (8), while models suggest ice sheets require millennia to approach equilibrium (9). Accordingly, sustained temperature increases from current emissions are expected to translate to long-term sea-level rise (SLR). Through modeling and with support from paleontological data, Levermann et al. (10) found a roughly linear global mean sea-level increase of 2.3 m per 1 °C warming within a time-envelope of the next 2,000 y.

This relationship forecasts a profound challenge in light of warming likely to exceed 2 °C given the current path of emissions (11). Although relatively modest in comparison, projected SLR of up to 1.2 m this century has been estimated to threaten up to 4.6% of the global population and 9.3% of annual global gross domestic product with annual flooding by 2100 in the absence of adaptive measures (12). Higher long-term sea levels endanger a fifth of all United Nations Educational, Scientific and Cultural Organization world heritage sites (13). These global analyses depend on elevation data with multimeter rms vertical errors that consistently overestimate elevation and thus underestimate submergence risk (14). Here we explore the challenges posed under different scenarios by long-term SLR in the United States, where highly accurate elevation and population data permit robust exposure assessments (15, 16).

Our analysis combines published relationships between cumulative carbon emissions and warming, together with two possible versions of the relationship between warming and sea level, to estimate global and regional sea-level commitments from different emissions totals. The first version, the “baseline” case, employs a minor modification of the warming–SLR relationship from Levermann et al. (10) The second version, the “triggered” case, makes a major adjustment to explore an important possibility suggested by recent research, by assuming that an inevitable collapse of the West Antarctic Ice Sheet (WAIS) already has been set in motion (1719).

For each case, we then use topographic, tidal, and census data to assess the contemporary populations living on implicated land nationwide, by state and by municipality. Although current populations will not experience full, long-term SLR, we use their exposure as a proxy for the challenge facing the more enduring built environment and the cultural and economic activity it embodies, given the strong spatial correlation between population and development. We focus most on cities, identifying and tabulating municipalities where committed sea levels would set land that is home to more than half (or other fractions) of the current population below the high tide line.

By “committed” or “locked in” warming or sea level in a given year, we refer to the long-term effects of cumulative anthropogenic carbon emissions through that year: the sustained temperature increase or SLR that will ensue on a time scale of centuries to millennia in the absence of massive and prolonged future active carbon removal from the atmosphere. We call a city “committed” when sea-level commitments would affect land supporting more than half of its current population (or another percentage of the population, if specified). We assume zero future emissions when assessing commitments for a given year, with the exception of one analysis incorporating future emissions implied by current energy infrastructure. When we associate years with warming, sea level, and city commitments, we are referencing the 21st century years when the commitments are established through cumulative emissions, not the years farther in the future when the commitments are realized through sustained temperature increases and SLR.

Warming Commitment

Numerous studies indicate a roughly linear relationship between total cumulative carbon emissions and century-scale global temperature increase, a ratio called the “transient climate response to carbon emissions” (36, 20). The Intergovernmental Panel on Climate Change (IPCC) judged a range of 0.8–2.5 °C per 1,000 gigatons of carbon (GtC) as 66% likely. For this study we prefer and use 0.7–2.0 °C, the 90% likely range from Gillett et al. (20), because it is observationally constrained. Furthermore, Gillett et al.’s central estimate of the transient response, 1.3 °C, very closely matches the 1.2 °C and 1.5 °C alternative IPCC estimates of warming per 1,000 GtC after 1,000 y from the end of emissions, assuming a midrange equilibrium climate sensitivity of 3 °C to the doubling of preindustrial carbon levels (6).

We estimate committed warming based on a distribution of possible transient response coefficient values from Gillett et al. and from future cumulative emissions under representative concentration pathways (RCPs) 2.6, 4.5, 6.0, and 8.5 (RCP Database version 2.0.5). For consistency, we approximate cumulative emissions through 2015 as 560 GtC based on historical values and forecasts under RCP 8.5 (21, 22); for a special case we add 199 GtC to this total to represent the future expectation of emissions already implicit in the current global energy infrastructure (23). Results range from 0.8 °C (0.5–1.0 °C) warming above preindustrial global temperature, committed by historic emissions, through 3.3 °C (2.3–4.2 °C), for RCP 8.5 through 2100 (see Table S1 for further information). We report 66% confidence intervals (CIs) for all quantities throughout this paper.

Table S1.

Total US municipalities becoming locked in so that 25, 50, or 100% of their 2010 population-weighted area will fall below the future committed high tide line, making no assumption about WAIS collapse (baseline case)

Emissions end date Emissions scenario Cumulative emissions, GtC Committed warming, °C (CI) Committed SLR, m (CI) Committed US municipalities–baseline case for WAIS
With 25% threshold With 50% threshold With 100% threshold
All municipalities (CI) >100,000 residents (CI) All municipalities (CI) >100,000 residents (CI) All municipalities (CI) >100,000 residents (CI)
2015 Historical 560 0.8 (0.5–1.0) 1.6 (0.0–3.7) 675 (0–1,261) 14 (0–25) 414 (0–942) 6 (0–17) 14 (0–199) 0 (0–2)
2015+ Historical + EIEI 800 1.0 (0.7–1.3) 2.2 (0.4–4.0) 846 (165–1,335) 17 (2–26) 604 (92–1,011) 8 (2–19) 38 (8–283) 0 (0–3)
2050 RCP 2.6 802 1.1 (0.8–1.4) 2.3 (0.6–4.1) 889 (227–1,347) 15 (2–26) 636 (119–1,028) 9 (2–19) 50 (8–283) 0 (0–3)
RCP 4.5 940 1.3 (0.9–1.6) 2.7 (0.9–4.4) 989 (361–1,396) 19 (2–26) 699 (208–1,082) 11 (2–19) 84 (11–330) 0 (0–3)
RCP 6.0 913 1.2 (0.9–1.6) 2.6 (0.8–4.3) 973 (341–1,387) 18 (2–26) 682 (190–1,071) 11 (2–19) 83 (9–315) 0 (0–3)
RCP 8.5 1110 1.5 (1.1–1.9) 3.1 (1.3–5.0) 1,121 (528–1,499) 22 (7–27) 809 (335–1,175) 16 (2–21) 128 (11–384) 0 (0–4)
2100 RCP 2.6 840 1.1 (0.8–1.5) 2.4 (0.7–4.2) 919 (273–1,362) 15 (2–26) 655 (140–1,043) 11 (2–19) 83 (8–283) 0 (0–3)
RCP 4.5 1,266 1.7 (1.2–2.2) 3.6 (1.7–5.6) 1,232 (713–1,575) 24 (15–28) 911 (460–1,272) 17 (7–22) 199 (14–470) 2 (0–5)
RCP 6.0 1,678 2.3 (1.6–2.9) 5.0 (2.7–7.2) 1,490 (1,057–1,826) 27 (21–42) 1,176 (756–1,479) 21 (15–24) 386 (126–683) 4 (0–7)
RCP 8.5 2,430 3.3 (2.3–4.2) 7.1 (4.3–9.9) 1,894 (1,504–2,176) 44 (27–53) 1,544 (1,185–1,812) 25 (21–35) 741 (411–1,021) 8 (4–13)
Not applicable Fixed warming Not applicable 1.5 2.9 (1.6–4.2) 1,042 (612–1,369) 21 (12–26) 744 (372–1,052) 15 (4–19) 103 (14–284) 0 (0–3)
2.0 4.7 (3.0–6.3) 1,441 (1,054–1,736) 27 (21–36) 1,119 (748–1,392) 20 (15–23) 353 (121–610) 4 (0–6)
3.0 6.4 (4.7–8.2) 1,770 (1,460–2,024) 39 (27–46) 1,415 (1,127–1,677) 23 (20–30) 653 (355–869) 6 (4–11)
4.0 8.9 (6.9–10.8) 2,101 (1,841–2,339) 49 (42–54) 1,748 (1,499–1,938) 34 (25–37) 943 (714–1,134) 12 (7–14)

Projections assume zero additional emissions after emissions end dates listed, except for the historical + EIEI scenario. EIEI is the expected future emissions implied by existing energy infrastructure, as estimated in ref. 23. The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. CIs are shown spanning 17th–83rd percentiles, the 66% (“likely”) range. Committed warming is in reference to the preindustrial global mean temperature, and committed SLR is in reference to global mean sea level in 1992. Note: the relationship between committed warming and committed SLR is different for fixed warming vs. all other scenarios, because all other scenarios involve distributions of warming amounts, and warming translates nonlinearly into SLR.

Sea-Level Commitment

We quantify sea-level commitment in the baseline case by building on Levermann et al. (10), who used physical simulations to model the SLR within a 2,000-y envelope as the sum of the contributions of (i) ocean thermal expansion, based on six coupled climate models; (ii) mountain glacier and ice cap melting, based on surface mass balance and simplified ice dynamic models; (iii) Greenland ice sheet decay, based on a coupled regional climate model and ice sheet dynamic model; and (iv) Antarctic ice sheet decay, based on a continental-scale model parameterizing grounding line ice flux in relation to temperature. Individual model parameterizations were constrained by paleontological data, and the overall modeled relationship between global temperature and sea level matched well against records from four previous warm periods: preindustrial, the last interglacial, marine isotope stage 11, and the mid-Pliocene.

The first three relationships from Levermann et al. (10) are monotonic, and we adopt them without modification. However, the wide range and finite number of simulation outputs render modeled relationships between temperature and Antarctic sea-level contribution locally nonmonotonic. The expected increase in Antarctic snowfall with warming could explain ice volume growth, but it is fair to assume that ice loss processes prevail in warmer climates (11). Here we define the future Antarctic ice volume loss committed for a global mean temperature increase T as the minimum loss across all temperature increases of T or greater. We apply this function to the median, 17th, and 83rd percentile curves from figure 2D in ref. 10 and thereby derive monotonic curves for minimum Antarctic sea-level contributions as a function of T.

To estimate uncertainty in total committed rise given some temperature increase, we use the derived Antarctic intervals, plus the ranges for the first three SLR components as shown in figure 2 A–C of ref. 10, as 17th/83rd percentile CIs from independent Gaussian distributions, a conservative simplifying assumption in that it narrows overall uncertainty compared with assuming any correlation. This method is commonly used, e.g., by the IPCC (11). To enable the assessment of a wide range of possible futures, we analyze 41 evenly spaced emissions totals from 500 to 2,500 GtC. For each total, we randomly sample 5,000 values of the transient response parameter assuming Gaussian distribution, compute warming levels, sample 5,000 random values from the distribution of each SLR component, given warming, and compute each component’s global median and variance from the 25 million values thus generated.

In this baseline case we find that cumulative emissions through 2015 already have locked in 1.6 m (0–3.7 m) of global SLR relative to the present level. Sea-level commitment rises to 2.2 m (0.4–4.0 m) after factoring in future emissions implied by the current energy infrastructure and reaches medians of 2.4 or 7.1 m by the end of the century under RCP 2.6 or 8.5, respectively. Table S1 presents results based on all four RCP scenarios through 2050 and 2100 and on a range of fixed temperature increases.

Our findings here illustrate the strong sensitivity of committed SLR to emissions (Fig. 1, baseline curve). Central estimates of the current marginal (gradient) effect of emitting 1 GtC are to add 1.9 mm of committed sea level. Equivalently, for each unit volume of petroleum combusted, roughly 400 units of ocean volume are added, based on the average carbon fuel density of contemporary US petroleum consumption (24).

Fig. 1.

Fig. 1.

Projections of long-term committed SLR as a function of cumulative carbon emissions, with 66% CIs, assuming (triggered case) or not assuming (baseline case) that eventual collapse of the WAIS is already inevitable.

WAIS Collapse

Remote sensing studies indicate accelerating decay, plus bedrock topography favorable to collapse, for the Thwaites and Pine Island glaciers, two linchpins of the WAIS (18). Recent modeling work also points toward future collapse, even at reduced rates of warming and decay from the present (19). Topographic analysis (25) together with theory (26, 27) and expert judgment (28, 29) indicate that the highly interconnected marine component of West Antarctica is prone to marine ice sheet instability that would spread throughout the entire basin following the disintegration of the Thwaites and Pine Island glaciers. In light of the magnitude of such an event, we include a special triggered case in our analysis to represent the possibility that collapse already is inevitable. The baseline case includes the possibility of WAIS instability, depending upon emissions and warming; the triggered case differs only in enforcing collapse under any scenario at some time within Levermann et al.’s (10) 2,000-y envelope.

It is important to note that simulations suggesting destabilization of the Thwaites and Pine Island glaciers (17, 19) have been validated, at most, against a two-decade record, because historic data for West Antarctica are limited. Circumpolar deep-water circulation patterns appear to be driving recent WAIS decline (30, 31), but again the record of these patterns is sparse and brief and shows considerable variability, with no clear linkage to greenhouse gas forcing (19, 3234). Nor is it completely certain that the loss of the Thwaites and Pine Island glaciers would lead to full WAIS destabilization. Accordingly, assumptions of complete West Antarctic collapse may be premature; however, we explore the triggered case because of its major potential impact.

The development and analysis of the triggered case is identical to the baseline case in every way except for the relationship between committed warming and the sea-level contribution from Antarctica. The Antarctic simulations used in Levermann et al. (10) do not isolate sea-level contribution subtotals from the WAIS, which has a total sea-level content of ∼3.3 m (25). The triggered case thus screens out all Antarctic simulations contributing less than 3.3 m, because these could not include total WAIS collapse. [We assume the loss of the West Antarctic ice mass initially dominates over other losses of Antarctic ice mass, as is currently the case (35).] Remaining simulation outputs are divided into 0.2 °C bins to recompute the median, 17th, and 83rd percentile values of total Antarctic contributions. From here we revert again to the methodology used for the baseline case, rendering Antarctic contributions monotonic with respect to temperature and then taking random samples from the distributions of the transient response coefficient and of SLR components to develop overall relationships of SLR to emissions and their uncertainty (Fig. S1).

Fig. S1.

Fig. S1.

Antarctic (Upper Row) and total (Lower Row) projections of committed SLR, given cumulative emissions and the baseline or triggered assumption regarding WAIS collapse. Blue lines and shading represent central and 66% CI estimates based on SLR sensitivity to warming, holding constant the transient climate response to emissions at its median value. Red lines and shading represent the central and 66% CI estimates based on warming sensitivity to the transient response, holding constant the sensitivity of SLR to warming at its median value.

Above 2,000 GtC, the triggered and baseline cases are very similar, because there is enough warming to make WAIS collapse highly likely even under the baseline case. Below 1,500 GtC, results from the two cases diverge significantly, with much larger committed global sea levels when collapse is already assumed (Fig. 1). The triggered case accordingly implies a weaker relationship between future emissions and long-term SLR. The present marginal effect of emitting 1 GtC under the triggered case is roughly 0.6 mm of locked-in sea level, or about 125 units of added ocean volume per unit volume of petroleum combusted. Table S2 presents sea-level commitments for the triggered case under a range of scenarios.

Table S2.

Total US municipalities becoming locked in so that 25, 50, or 100% of their 2010 population-weighted area will fall below the future committed high tide line, assuming inevitable collapse of the WAIS under any scenario (triggered case)

Emissions end date Emissions scenario Cumulative emissions, GtC Committed warming, °C (CI) Committed SLR, m (CI) Committed US municipalities–triggered case for WAIS
With 25% threshold With 50% threshold With 100% threshold
All municipalities >100,000 residents All municipalities >100,000 residents All municipalities >100,000 residents
2015 Historical 560 0.8 (0.5–1.0) 4.6 (3.5–5.8) 1,475 (1,261–1,690) 27 (25–33) 1,153 (931–1,343) 20 (17–23) 370 (199–553) 4 (2–6)
2015+ Historical + EIEI 800 1.0 (0.7–1.3) 4.8 (3.8–5.8) 1,516 (1,335–1,697) 27 (26–34) 1,202 (1,011–1,356) 22 (19–23) 426 (283–582) 4 (3–6)
2050 RCP 2.6 802 1.1 (0.8–1.4) 4.9 (3.9–5.8) 1,528 (1,348–1,704) 28 (26–34) 1,210 (1,025–1,357) 22 (19–23) 427 (283–583) 4 (3–6)
RCP 4.5 940 1.3 (0.9–1.6) 5.0 (4.0–6.0) 1,549 (1,365–1,713) 28 (26–34) 1,234 (1,046–1,372) 22 (19–23) 427 (283–590) 4 (3–6)
RCP 6.0 913 1.2 (0.9–1.6) 5.0 (4.0–6.0) 1,546 (1,363–1,712) 28 (26–34) 1,228 (1,046–1,371) 22 (19–23) 427 (283–590) 4 (3–6)
RCP 8.5 1,110 1.5 (1.1–1.9) 5.2 (4.1–6.2) 1,569 (1,376–1,747) 28 (26–37) 1,251 (1,056–1,399) 22 (19–23) 445 (300–611) 5 (3–6)
2100 RCP 2.6 840 1.1 (0.8–1.5) 4.9 (4.0–5.9) 1,536 (1,354–1,707) 28 (26–34) 1,216 (1,035–1,361) 22 (19–23) 427 (283–585) 4 (3–6)
RCP 4.5 1,266 1.7 (1.2–2.2) 5.3 (4.1–6.6) 1,581 (1,379–1,774) 28 (26–40) 1,271 (1,059–1,437) 22 (19–23) 472 (302–656) 5 (3–6)
RCP 6.0 1,678 2.3 (1.6–2.9) 5.9 (4.3–7.5) 1,704 (1,437–1,915) 34 (27–44) 1,358 (1,115–1,563) 23 (20–26) 585 (353–774) 6 (4–8)
RCP 8.5 2,430 3.3 (2.3–4.2) 7.4 (5.0–9.9) 1,957 (1,645–2,195) 46 (32–53) 1,596 (1,307–1,825) 27 (23–35) 796 (504–1024) 8 (5–13)
Not applicable Fixed warming Not applicable 1.5 5.2 (4.4–6.0) 1,560 (1,410–1,710) 28 (27–34) 1,249 (1,097–1,369) 22 (20–23) 443 (345–590) 5 (4–6)
2.0 5.7 (4.5–7.0) 1,666 (1,445–1,864) 32 (27–42) 1,327 (1,123–1,516) 23 (20–25) 537 (353–735) 6 (4–7)
3.0 6.9 (5.3–8.5) 1,839 (1,575–2,042) 42 (28–48) 1,499 (1,277–1,700) 25 (22–32) 709 (461–894) 7 (5–11)
4.0 9.4 (7.5–11.3) 2,150 (1,927–2,374) 52 (44–54) 1,798 (1,575–1,978) 34 (26–37) 995 (794–1,160) 12 (8–14)

EIEI is the expected future emissions implied by existing energy infrastructure, as estimated in ref. 23. The years shown relate to emissions and associated commitments, not to the timing of the ensuing warming or SLR. See the legend of Table S1 for further documentation.

Effects on Cities and Populated Land

Future sea levels committed under each of the emissions and Antarctic scenarios considered present serious implications for US coastal regions. To assess these implications, we translate global into local SLR projections using a model of spatial variation in sea-level contributions caused by isostatic deformation and changes in gravity as the Greenland and Antarctic ice sheets lose mass (3638), represented as two global 0.5° matrices of scalar adjustment factors to the ice sheets’ respective median global contributions to SLR and (squared) to their variances. We then derive gridded medians and CIs for local committed SLR including all components, based on cumulative emissions and ice sheet case.

To develop metrics for municipal commitments, we estimate, relative to the high tide line, the elevation below which is land that is home to 25, 50, or 100% of the 2010 population for each coastal municipality of any size in the United States. We use these heights as indicators of committed SLR likely to pose existential threats to the built cultural legacy of each locality as it exists today. We tabulate the cities where, by scenario and over time, the committed local sea level crosses these thresholds at lower, central, and upper SLR projections, further localized from the global 0.5° grid to city centroids using bilinear interpolation. We call the emissions levels corresponding to threshold sea levels the “critical cumulative emissions” for each municipality, and estimate whether and when these levels are reached under different emissions scenarios and ice sheet cases.

We also assess by county the total current population living on land exposed to different committed local sea levels, based on bilinear interpolation of projections to county centroids, and combine county results into state and national totals.

To assess topography as required for this analysis, we use LIDAR-based digital elevation models compiled and distributed by the National Oceanic and Atmospheric Administration (NOAA) (coast.noaa.gov/digitalcoast). We then recompute elevations relative to mean higher high water (MHHW) levels at nearest neighbors in NOAA’s VDatum grid (vdatum.noaa.gov). To include Alaska, we use the National Elevation Dataset (nationalmap.gov/elevation.html) and a global grid for MHHW (provided by Mark Merrifield, University of Hawaii, Manoa, Hawaii) developed using the model TPXO8 (39). We use US census block boundaries and populations to determine localized population densities and municipality (census “place”) and county boundaries for assessing threats at municipal through national levels (www.census.gov/geo/maps-data/data/tiger-line.html).

For each municipality and county we compute the population living 0.5–15 m below MHHW in increments of 0.5 m, assuming census blocks of uniform density, except for zero density over wetland areas (16). We interpolate each elevation–population relationship to estimate county populations on affected land at sea levels of interest and to estimate the thresholds below which selected fractions of each city population (i) live. We label the threshold for half of population as hi50%. Each city’s centroid coordinates, lati and loni, and the West Antarctic case x, then determine the smallest temperature Txi such that SLRx(Txi,lati,loni)0.16hi50%. The 0.16-m adjustment to projections of SLR above the preindustrial level reflects estimates of global mean SLR from the late 19th century through 1992 (40). 1992 is the midpoint of the reference period used to define MHHW at most US tide gauges, creating a match with our population analysis. We use 1992 global mean sea level as the “present” reference for all SLR projections reported here.

Calling CS(t) the cumulative carbon released under emissions scenario S by year t, each city’s “commitment date,” txiS, then is determined as the earliest year for which the locked-in SLR exceeds the critical elevation threshold, i.e., when the product of the transient climate response with CS(t) exceeds Txi. CS(txiS) is the critical cumulative emissions level.

Results

In the baseline case, without any special assumptions concerning West Antarctica, cumulative emissions through 2015 commit SLR that translates to 414 (0–942) US municipalities where more than 50% of the population-weighted area will fall below the future high tide line. City commitments climb to 604 (92–1,011) after accounting for future emissions implied by current energy infrastructure. The same sea levels would cover land where a total of 6.2 (0.0–15.1) million people live today across all coastal US states, or where 9.5 (0.0–17.4) million people live after accounting for emissions expected from infrastructure.

Median commitments from purely historic emissions are much larger under the triggered case, at 1,153 municipalities and 19.8 million people, with current energy infrastructure adding less than 5% marginal increases beyond these higher base levels.

Although starting from different points, the total commitments for both the baseline and triggered cases climb with accumulating future emissions (Fig. 2). Commitments within each case begin to diverge after 2030 depending upon the emissions scenario and diverge strongly after midcentury. However, business-as-usual emissions through 2100 (RCP 8.5) lead to similar final results under either Antarctic case, with 1,544 or 1,596 municipalities, respectively, committed at 50% (union of confidence intervals, 1,185–1,825), affecting land that is home to current populations of 26.3 or 27.4 million people (union of intervals 20.6–32.1 million). These patterns arise because at high emissions levels the total Antarctic contribution to SLR equals or exceeds the sea-level content of the WAIS in most simulations, so very few simulations must be filtered out from the triggered case, making it nearly identical to the baseline case. The slopes of change from low- to high-emissions scenarios (or for any addition to historic emissions) are greater for the baseline case, because it starts from a lower point.

Fig. 2.

Fig. 2.

Projections of committed global SLR (Left) and municipalities where more than half the population-weighted area would be affected (Right), under different emissions scenarios and assumptions about West Antarctica. The years shown relate to emissions and associated commitments, not to the timing of ensuing SLR. The 66% CIs are shown for the baseline Antarctic case only.

Contrasted with the high-emissions scenario RCP 8.5, aggressive curtailment of emissions under RCP 2.6 can lead to the avoidance of commitment for nearly 900 US municipalities, and, more broadly, for land that is home to 15.8 million people in the baseline case, using central estimates, and for nearly 400 municipalities and land that is home for 6.6 million people assuming WAIS collapse. Intermediate scenarios yield intermediate results; Table 1 gives details. Fourteen cities with more than 100,000 contemporary residents can avoid locking in this century; the largest include Jacksonville and St. Petersburg in Florida; Chesapeake, Norfolk, and Virginia Beach in Virginia; and Sacramento and Stockton in California (Fig. 3). Under RCP 8.5, a median of 25 cities this large would be committed under the baseline case, and 27 cities of this size would be committed under the triggered case.

Table 1.

US municipalities and populated land avoiding commitment under different carbon emissions scenarios compared with RCP 8.5

Emissions end year WAIS assumption Avoidable commitments by emissions scenario
RCP 2.6 RCP 4.5 RCP 6.0
Municipalities (count >50% committed)
2050 Baseline 170 107 124
2050 Triggered 41 17 23
2100 Baseline 889 633 368
2100 Triggered 380 325 238
Populated land (2010 population, in millions of persons)
2050 Baseline 3.5 2.0 2.3
2050 Triggered 0.8 0.4 0.5
2100 Baseline 15.8 11.1 6.4
2100 Triggered 6.6 5.6 4.0

Values are based on differences between median estimates; see text for a description of WAIS assumptions.

Fig. 3.

Fig. 3.

State and total populations on land and major cities in which the majority of the population occupies land committed to fall below future high tide lines given emissions through 2100 under RCP 2.6 (blue city markers on both maps) or 8.5 (red city markers) and assuming the baseline Antarctic case (see text). Only implicated cities with total populations exceeding 100,000 are shown; the marker radius is proportional to the total city population, ranging from 105,162 (Cambridge, MA) to 819,050 (Jacksonville, FL) persons. Table S4 lists all plotted cities by name and provides the critical cumulative emissions totals needed for commitment and the corresponding commitment years under all four RCP scenarios. The five most populated cities are labeled here in descending order: JAC, Jacksonville, FL; SAC, Sacramento, CA; VB, Virginia Beach, VA; MIA, Miami; and NO, New Orleans. Table S8 lists individual state values for all scenarios, including Alaska and Hawaii, which are not shown here but are included in the coastal states’ totals.

Using a pure temperature-based reference frame, the United Nations Framework Convention on Climate Change’s Cancun Agreement target of 2 °C warming would translate to 1,119 (748–1,392) or 1,327 (1,123–1,516) cities committed under the baseline or triggered assumptions, respectively, and would affect land that is home to 19.0 (11.6–25.0) or 23.0 (16.8–28.1) million people today, respectively. Warming of 4 °C would increase central estimates to more than 1,745 cities and 30 million people under either assumption.

Under all scenarios, Florida has the plurality or majority of committed cities with total population greater than 100,000. Under all but the two most extreme scenarios (fixed 4 °C warming or RCP 8.5 through 2100), Florida holds 40% or more of the population living on potentially affected land. After Florida, the next three most affected states are California, Louisiana, and New York, in different orders for different scenarios, reflecting the wide geographic distribution of the SLR commitment challenge.

For more extensive details, Tables S1 (baseline) and S2 (triggered) present broken-out results including projections of committed sea levels based on historical emissions, four RCP scenarios through 2050 and 2100, and fixed warming amounts from 1.5 to 4 °C; tabulations of all municipalities locking in at these sea levels, using 25, 50, and 100% commitment thresholds; and tabulations limited to large cities. Tables S3S6 list the individual large cities committed at different thresholds under each emissions scenario and ice sheet case, by year. Tables S7S9 (baseline case) and S10S12 (triggered case) show the population living on implicated land, by state and for the US total of coastal states, under all emissions and temperature scenarios and time frames.

Table S3.

Cities exceeding 100,000 residents where 25% of the 2010 population-weighted area will fall below the future committed high tide line, making no assumption about WAIS collapse (baseline case)

City State Total population Population rank Critical cumulative emissions, GtC Committed SLR, m Commitment year
RCP 8.5 RCP 6.0 RCP 4.5 RCP 2.6
Beaumont TX 118,286 37 1,840 5.4 2080
Boston MA 617,594 3 930 2.8 2045 2055 2050
Bridgeport CT 144,229 26 2,070 6.2 2090
Brownsville TX 175,023 21 2,260 6.9 2095
Cambridge MA 105,162 42 AE 1.5 AE AE AE AE
Cape Coral FL 153,809 24 590 1.9 2020 2020 2020 2020
Charleston SC 119,875 36 AE 1.6 AE AE AE AE
Chesapeake VA 221,576 17 980 2.9 2045 2060 2055
Clearwater FL 107,685 38 1,970 6.0 2085
Coral Springs FL 121,062 35 900 2.8 2040 2050 2050
Corpus Christi TX 305,184 11 1,870 5.6 2085
Elizabeth NJ 124,969 33 1,910 5.7 2085
Elk Grove CA 152,772 25 1,860 5.5 2080
Fort Lauderdale FL 165,521 22 AE 1.2 AE AE AE AE
Hampton VA 137,373 30 910 2.7 2040 2050 2050
Hayward CA 142,760 27 2,140 6.5 2090
Hialeah FL 224,634 16 AE 1.5 AE AE AE AE
Hollywood FL 139,946 28 AE 1.5 AE AE AE AE
Honolulu (Urban) HI 337,248 9 1,210 3.9 2055 2075 2090
Huntington Beach CA 189,992 19 AE 1.1 AE AE AE AE
Jacksonville FL 819,050 2 1,720 5.1 2075
Jersey City NJ 247,597 13 1,270 3.7 2060 2075
Long Beach CA 458,815 5 2,010 6.1 2090
Metairie LA 138,481 29 AE 0.1 AE AE AE AE
Miami FL 399,457 7 AE 1.7 AE AE AE AE
Miami Gardens FL 107,167 40 AE 1.6 AE AE AE AE
Miramar FL 107,278 39 AE 1.2 AE AE AE AE
New Haven CT 129,779 32 2,400 7.2 2100
New Orleans LA 343,467 8 AE 0.2 AE AE AE AE
New York NY 8,175,083 1 2,160 6.5 2095
Newport News VA 180,659 20 2,070 6.3 2090
Norfolk VA 242,751 15 900 2.7 2040 2050 2050
Oxnard CA 197,820 18 2,190 6.7 2095
Palm Bay FL 103,190 44 2,220 6.8 2095
Pembroke Pines FL 123,802 34 AE 1.3 AE AE AE AE
Port St. Lucie FL 164,438 23 1,550 4.6 2070 2095
Richmond CA 103,668 43 2,410 7.4 2100
Sacramento CA 466,486 4 1,100 3.2 2050 2065 2070
Savannah GA 136,286 31 1,220 3.5 2060 2075 2090
St. Petersburg FL 244,767 14 AE 1.7 AE AE AE AE
Stockton CA 277,588 12 AE 1.4 AE AE AE AE
Tampa FL 335,654 10 1,380 4.0 2065 2085
Virginia Beach VA 436,497 6 950 2.9 2045 2055 2055
Wilmington NC 106,476 41 2,120 6.4 2090

The alphabetical list includes the SLR increment required for each city to commit at 25%, together with the corresponding central estimate of critical cumulative emissions. Committed SLR in turn corresponds to these emissions. AE indicates that historical emissions already have exceeded the critical level. Where applicable, RCP columns indicate future 21st century years (rounded to the nearest multiple of 5) when different RCPs will exceed each city’s critical emissions level. The years shown relate to emissions and associated commitments, not to the timing of the ensuing warming or SLR. Rows for the 10 largest cities are shaded.

Table S6.

Cities exceeding 100,000 residents where 50 or 100% of the 2010 population-weighted area will fall below the future committed high tide line, assuming inevitable collapse of the WAIS under any emissions scenario (triggered case)

City State Total population Population rank Critical cumulative emissions, GtC Committed SLR, m Commitment year
RCP 8.5 RCP 6.0 RCP 4.5 RCP 2.6
Commitment threshold: 50%
 Beaumont TX 118,286 23 1,990 6.6 2085
 Cambridge MA 105,162 26 AE 2.8 AE AE AE AE
 Cape Coral FL 153,809 14 AE 2.5 AE AE AE AE
 Charleston SC 119,875 22 AE 2.4 AE AE AE AE
 Chesapeake VA 221,576 10 AE 4.0 AE AE AE AE
 Coral Springs FL 121,062 21 AE 3.1 AE AE AE AE
 Elk Grove CA 152,772 15 2,410 7.6 2100
 Fort Lauderdale FL 165,521 12 AE 1.6 AE AE AE AE
 Hampton VA 137,373 18 AE 2.9 AE AE AE AE
 Hialeah FL 224,634 9 AE 1.7 AE AE AE AE
 Hollywood FL 139,946 16 AE 2.1 AE AE AE AE
 Huntington Beach CA 189,992 11 AE 3.4 AE AE AE AE
 Jacksonville FL 819,050 1 2,130 7.0 2090
 Metairie LA 138,481 17 AE 0.3 AE AE AE AE
 Miami FL 399,457 4 AE 2.5 AE AE AE AE
 Miami Gardens FL 107,167 25 AE 1.8 AE AE AE AE
 Miramar FL 107,278 24 AE 1.6 AE AE AE AE
 New Orleans LA 343,467 5 AE 0.3 AE AE AE AE
 Norfolk VA 242,751 8 AE 2.9 AE AE AE AE
 Palm Bay FL 103,190 27 2,270 7.5 2095
 Pembroke Pines FL 123,802 20 AE 1.6 AE AE AE AE
 Port St. Lucie FL 164,438 13 1,410 5.8 2065 2085
 Sacramento CA 466,486 2 730 5.0 2030 2035 2035 2035
 Savannah GA 136,286 19 590 4.9 2020 2020 2020 2020
 St. Petersburg FL 244,767 7 AE 4.6 AE AE AE AE
 Stockton CA 277,588 6 AE 2.8 AE AE AE AE
 Virginia Beach VA 436,497 3 AE 3.9 AE AE AE AE
Commitment threshold: 100%
 Cape Coral FL 153,809 3 1,570 6.0 2070 2095
 Hialeah FL 224,634 2 AE 3.5 AE AE AE AE
 Hollywood FL 139,946 4 2,020 7.0 2090
 Metairie LA 138,481 5 AE 3.5 AE AE AE AE
 Miami Gardens FL 107,167 8 1,030 5.5 2050 2060 2060
 Miramar FL 107,278 7 2,230 7.5 2095
 New Orleans LA 343,467 1 AE 4.5 AE AE AE AE
 Pembroke Pines FL 123,802 6 AE 4.0 AE AE AE AE

The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. Rows for the 10 largest cities are shaded underneath each commitment threshold level. See the legend of Table S3 for further documentation.

Table S7.

Coastal state and US total 2010 census populations living on land falling below future committed high tide lines under different emissions scenarios through 2050, making no assumptions about the inevitability of WAIS collapse (baseline case)

State Population (in thousands of persons) living below committed sea levels by scenario: median (white) and 17th–83rd percentile estimates (shaded)
Historical emissions Historical + EIEE RCP 2.6 through 2050 RCP 4.5 through 2050 RCP 6.0 through 2050 RCP 8.5 through 2050
Alaska 29 0–40 33 1–44 33 22–45 35 25–48 35 24–48 37 27–52
Alabama 12 0–42 20 0–51 21 1–52 27 4–57 26 3–56 35 8–63
California 587 0–1,377 836 0–1,608 876 242–1,644 1,013 321–1,765 981 303–1,736 1,208 446–1,943
Connecticut 47 0–125 72 0–151 76 0–156 89 16–171 86 14–167 108 30–192
District of Columbia 1 0–8 3 0–12 3 0–12 5 1–14 4 1–14 7 1–17
Delaware 23 0–58 34 0–71 36 1–73 42 8–81 41 7–79 50 16–91
Florida 2,465 0–6,556 4,268 0–7,360 4,535 220–7,492 5,177 497–7,965 5,029 433–7,854 5,978 1,296–8,594
Georgia 65 0–216 107 0–266 114 10–274 138 22–300 132 20–294 177 40–332
Hawaii 100 0–219 153 4–243 159 6–246 180 17–260 176 12–257 204 65–278
Louisiana 1,098 0–1,507 1,242 0–1,628 1,264 741–1,647 1,331 849–1,709 1,316 825–1,696 1,422 985–1,790
Massachusetts 223 0–496 330 0–558 344 3–568 389 67–600 379 60–593 446 136–645
Maryland 67 0–182 103 0–219 109 4–225 130 24–244 125 21–240 157 43–272
Maine 7 0–22 11 0–27 12 0–28 15 2–31 14 2–30 18 4–35
Mississippi 14 0–65 23 0–84 25 2–87 34 5–98 32 4–95 50 9–117
North Carolina 126 0–284 180 0–325 189 28–331 216 52–353 210 47–348 253 90–385
New Hampshire 6 0–12 8 0–14 8 0–14 9 2–15 9 2–15 11 4–17
New Jersey 338 0–742 482 0–846 504 8–863 573 108–918 558 92–905 662 223–997
New York 411 0–1,320 710 0–1,616 758 2–1,662 909 82–1,815 876 68–1,782 1,116 221–2,019
Oregon 13 0–29 18 0–35 19 5–36 22 7–38 21 6–38 26 10–42
Pennsylvania 10 0–54 17 0–78 19 0–83 27 3–97 25 3–93 40 6–116
Rhode Island 10 0–34 17 0–42 18 0–44 22 3–48 21 3–47 28 6–54
South Carolina 134 0–363 205 0–431 216 18–442 257 45–479 247 40–471 313 88–530
Texas 155 0–419 236 0–512 250 35–529 296 60–586 285 55–572 360 105–675
Virginia 168 0–847 333 0–1,021 366 20–1,042 494 46–1,109 464 41–1,095 685 96–1,193
Washington 74 0–130 92 0–146 95 32–149 105 48–157 103 46–155 118 62–167
  US total 6,181 0–15,148 9,533 4–17,388 10,052 1,400–17,743 11,535 2,314–18,959 11,194 2,132–18,678 13,508 4,017–20,617

Projections assume zero additional emissions after emissions end dates listed, except for the historical + EIEI scenario. EIEI is the expected future emissions implied by existing energy infrastructure, as estimated in ref. 23. The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. Levels of committed warming and SLR associated with each scenario are shown in Table S1. US totals include only the listed states and the District of Columbia.

Table S9.

Coastal state and US total 2010 census populations living on land falling below future committed high tide lines under different fixed long-term warming scenarios, making no assumptions about the inevitability of WAIS collapse (baseline case)

State Population (in thousands of persons) living below committed sea levels by scenario: median (white) and 17th–83rd percentile estimates (shaded)
1.5 °C warming 2 °C warming 3 °C warming 4 °C warming
Alaska 36 26–50 48 35–60 58 46–70 72 60–82
Alabama 31 5–60 57 27–85 82 53–120 130 87–174
California 1,097 372–1,842 1,775 1,025–2,512 2,441 1,706–3,179 3,360 2,626–4,043
Connecticut 97 20–179 169 88–255 236 149–321 323 238–401
Dist. of Columbia 5 1–15 14 4–23 22 12–29 30 23–38
Delaware 45 11–85 80 42–130 118 71–183 188 122–257
Florida 5,540 761–8,250 8,010 5,244–9,926 9,755 7,679–10,996 11,168 10,019–11,827
Georgia 153 28–314 300 138–391 383 277–420 424 391–441
Hawaii 191 37–268 265 187–321 320 264–366 384 339–420
Louisiana 1,370 909–1,744 1,710 1,332–2,015 1,979 1,665–2,212 2,253 2,032–2,433
Massachusetts 412 84–618 596 384–774 732 550–912 912 732–1,091
Maryland 141 30–256 242 128–368 343 219–451 457 351–560
Maine 16 3–32 30 14–50 44 26–67 67 44–90
Mississippi 40 6–106 99 34–175 165 90–234 243 180–263
North Carolina 232 66–366 353 216–496 469 331–640 658 488–782
New Hampshire 10 3–16 15 9–22 20 14–28 28 20–35
New Jersey 609 147–950 912 566–1,229 1,164 842–1,466 1,480 1,177–1,798
New York 991 116–1,897 1,799 893–2,635 2,453 1,599–3,290 3,321 2,483–4,131
Oregon 24 8–40 38 22–52 51 36–70 74 53–88
Pennsylvania 32 4–104 95 25–184 161 77–280 285 165–390
Rhode Island 24 4–51 48 22–75 68 41–97 98 68–129
South Carolina 280 59–500 478 256–670 644 445–777 794 667–892
Texas 323 76–623 588 298–1,009 959 549–1,501 1,637 1,057–2,190
Virginia 571 61–1,145 1,108 491–1,373 1,342 1,035–1,463 1,473 1,359–1,620
Washington 111 54–161 157 105–198 192 150–243 254 200–312
  US total 12,383 2,893–19,673 18,984 11,584–25,030 24,202 17,929–29,414 30,114 24,982–34,487

Pure warming scenarios assume long-term fixed warming levels, and make no predictions about the timing of ensuing SLR. Levels of committed SLR associated with each scenario are shown in Table S1. US totals include only the listed states and the District of Columbia.

Table S10.

Coastal state and US total 2010 census populations living on land falling below future committed high tide lines under different emissions scenarios through 2050, assuming the inevitable collapse of the WAIS under any scenario (triggered case)

State Population (in thousands) living below committed sea levels by scenario: median (white) and 17th–83rd percentile estimates (shaded)
Historical emissions Historical + EIEE RCP 2.6 through 2050 RCP 4.5 through 2050 RCP 6.0 through 2050 RCP 8.5 through 2050
Alaska 50 37–61 52 38–62 52 38–62 52 39–63 52 39–63 53 39–64
Alabama 59 32–87 62 36–90 63 36–90 64 38–92 64 37–91 66 40–94
California 1,835 1,126–2,539 1,922 1,221–2,627 1,936 1,237–2,641 1,975 1,281–2,682 1,967 1,272–2,673 2,025 1,336–2,732
Connecticut 182 102–263 191 111–272 193 112–274 197 116–278 196 115–277 203 121–284
Dist. of Columbia 15 6–24 17 7–25 17 7–25 18 7–25 18 7–25 18 8–25
Delaware 86 48–136 91 52–142 92 52–144 94 54–147 94 54–146 97 56–151
Florida 8,297 5,751–10,003 8,572 6,105–10,160 8,617 6,162–10,185 8,748 6,313–10,262 8,719 6,283–10,245 8,903 6,482–10,358
Georgia 314 159–393 329 180–397 331 184–398 337 194–400 336 191–399 344 206–402
Hawaii 272 201–323 280 211–329 281 212–330 285 217–332 284 216–332 289 222–336
Louisiana 1,740 1,383–2,025 1,779 1,427–2,056 1,785 1,434–2,061 1,802 1,455–2,075 1,798 1,450–2,072 1,824 1,481–2,091
Massachusetts 625 433–793 644 457–812 648 461–815 657 472–824 655 470–822 668 486–836
Maryland 257 148–377 269 160–390 272 162–392 278 168–397 276 166–396 286 175–404
Maine 33 17–53 35 19–55 35 19–56 36 20–57 36 20–57 37 21–58
Mississippi 106 43–179 114 51–188 116 52–189 120 56–194 119 55–193 125 61–199
North Carolina 368 242–508 383 259–529 386 261–532 393 269–542 391 267–540 402 278–554
New Hampshire 16 10–23 17 11–24 17 11–24 17 11–24 17 11–24 18 12–25
New Jersey 956 634–1,255 993 674–1,286 999 680–1,292 1,016 699–1,307 1,012 695–1,304 1,036 722–1,325
New York 1,917 1,051–2,711 2,010 1,148–2,800 2,025 1,164–2,815 2,069 1,211–2,858 2,059 1,201–2,849 2,122 1,267–2,911
Oregon 40 24–53 42 26–55 42 27–55 43 27–56 43 27–55 44 29–57
Pennsylvania 105 35–194 114 41–207 115 42–209 120 46–216 119 45–214 125 50–224
Rhode Island 52 27–78 54 29–81 55 30–81 56 31–83 56 31–83 58 33–85
South Carolina 501 292–678 525 318–694 529 323–696 540 335–704 538 332–702 554 350–712
Texas 618 332–1,027 661 363–1,080 669 368–1,089 692 382–1,115 687 379–1,109 721 400–1,149
Virginia 1,154 630–1,382 1,190 718–1,395 1,196 732–1,397 1,211 774–1,403 1,208 765–1,402 1,231 822–1,410
Washington 161 113–200 166 119–206 167 120–206 169 123–209 168 123–208 172 127–212
  US total 19,758 12,876–25,363 20,512 13,779–25,961 20,634 13,927–26,058 20,989 14,339–26,344 20,912 14,252–26,281 21,420 14,822–26,696

Projections assume zero additional emissions after emissions end dates listed, except for the historical + EIEI scenario. EIEI is the expected future emissions implied by existing energy infrastructure, as estimated in ref. 23. The years shown relate to emissions and associated commitments, not the timing of ensuing warming or SLR. Levels of committed warming and SLR associated with each scenario are shown in Table S2. US totals include only the listed states and the District of Columbia.

Table S12.

Coastal state and US total 2010 census populations living on land falling below future committed high tide lines under different fixed long-term warming scenarios, assuming the inevitable collapse of the WAIS under any scenario (triggered case)

State Population (in thousands of persons) living below committed sea levels by scenario: median (white) and 17th–83rd percentile estimates (shaded)
1.5 °C warming 2 °C warming 3 °C warming 4 °C warming
Alaska 53 40–64 56 43–67 61 50–72 74 63–84
Alabama 67 40–94 75 48–105 89 62–132 143 96–179
California 2,035 1,346–2,741 2,235 1,552–2,943 2,639 1,933–3,339 3,546 2,848–4,134
Connecticut 204 122–285 225 142–306 258 177–339 344 264–416
District of Columbia 19 8–26 21 11–27 24 15–32 33 24–39
Delaware 98 57–152 110 67–168 134 85–199 206 141–271
Florida 8,924 6,512–10,375 9,422 7,193–10,714 10,119 8,513–11,191 11,380 10,449–11,921
Georgia 345 208–402 368 250–410 395 322–426 430 402–444
Hawaii 290 223–336 305 244–350 334 286–376 396 353–426
Louisiana 1,828 1,485–2,094 1,909 1,591–2,152 2,050 1,772–2,257 2,304 2,106–2,461
Massachusetts 669 488–837 712 537–882 779 610–951 959 787–1,128
Maryland 287 176–405 320 205–431 375 254–472 483 387–583
Maine 37 21–59 42 25–64 50 31–72 73 51–96
Mississippi 126 62–199 146 78–218 186 112–244 252 203–265
North Carolina 403 279–556 439 313–602 514 372–671 693 544–805
New Hampshire 18 12–25 20 13–27 22 16–29 30 23–37
New Jersey 1,039 725–1,328 1,119 810–1,404 1,243 943–1,537 1,564 1,268–1,863
New York 2,130 1,276–2,918 2,338 1,514–3,130 2,671 1,876–3,481 3,550 2,735–4,285
Oregon 44 29–57 48 33–63 54 41–74 78 58–90
Pennsylvania 125 50–225 147 69–256 190 102–305 315 200–408
Rhode Island 58 33–85 65 39–92 76 50–104 106 77–135
South Carolina 556 353–713 608 410–746 684 511–803 825 709–908
Texas 726 404–1,156 847 482–1,309 1,078 659–1,640 1,795 1,208–2,231
Virginia 1,234 828–1,411 1,305 984–1,439 1,382 1,155–1,490 1,509 1,398–1,645
Washington 172 127–213 183 141–227 204 164–257 270 214–322
  US total 21,487 14,903–26,756 23,064 16,796–28,132 25,611 20,112–30,496 31,358 26,608–35,175

Pure warming scenarios assume long-term fixed warming levels, and make no predictions about the timing of ensuing SLR. Levels of committed SLR associated with each scenario are shown in Table S1. US totals include only the listed states and the District of Columbia.

Table S8.

Coastal state and US total 2010 census populations living on land falling below future committed high tide lines under different emissions scenarios through 2100, making no assumptions about the inevitability of WAIS collapse (baseline case)

State Population (in thousands of persons) living below committed sea levels by scenario: median (white) and 17th–83rd percentile estimates (shaded)
RCP 2.6 through 2100 RCP 4.5 through 2100 RCP 6.0 through 2100 RCP 8.5 through 2100
Alaska 34 23–46 40 30–54 50 36–61 63 51–74
Alabama 23 2–53 42 12–70 60 32–89 93 64–141
California 911 263–1,675 1,384 596–2,106 1,871 1,128–2,610 2,750 2,009–3,482
Connecticut 80 10–160 125 47–211 178 96–264 265 180–350
District of Columbia 4 1–13 8 1–20 15 5–24 24 16–33
Delaware 38 5–75 58 23–102 85 45–137 140 87–208
Florida 4,704 294–7,611 6,595 2,590–9,082 8,346 5,665–10,097 10,308 8,729–11,342
Georgia 120 16–281 216 65–355 316 155–395 400 332–430
Hawaii 165 8–250 223 110–292 276 201–328 343 294–388
Louisiana 1,283 773–1,664 1,507 1,100–1,860 1,752 1,379–2,047 2,085 1,801–2,294
Massachusetts 357 44–576 495 219–683 614 408–792 793 616–974
Maryland 115 15–230 181 66–299 255 140–381 386 261–487
Maine 13 2–28 21 7–39 32 16–52 52 31–75
Mississippi 27 3–90 65 14–133 108 42–185 196 119–250
North Carolina 196 35–337 285 127–415 368 234–517 535 381–692
New Hampshire 9 1–15 12 6–18 16 10–23 23 16–30
New Jersey 524 56–877 739 334–1,068 946 605–1,259 1,270 958–1,582
New York 801 38–1,703 1,312 404–2,203 1,886 981–2,720 2,744 1,912–3,599
Oregon 20 6–36 30 13–45 40 24–54 56 43–77
Pennsylvania 21 2–86 54 10–133 103 31–196 201 106–321
Rhode Island 19 2–45 34 10–60 50 24–78 78 51–108
South Carolina 227 28–452 363 134–576 503 284–686 701 526–823
Texas 262 43–543 420 156–770 633 331–1,067 1,147 699–1,754
Virginia 395 29–1,061 849 169–1,258 1,148 577–1,386 1,394 1,176–1,512
Washington 98 41–151 130 74–176 162 112–204 210 168–268
  US total 10,443 1,739–18,060 15,189 6,316–22,031 19,813 12,560–25,650 26,255 20,625–31,295

Projections assume zero additional emissions after emissions end dates listed. The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. Levels of committed warming and SLR associated with each scenario are shown in Table S1. US totals include only the listed states and the District of Columbia.

Table S11.

Coastal state and US total 2010 census populations living on land falling below future committed high tide lines under different emissions scenarios through 2100, assuming the inevitable collapse of the WAIS under any scenario (triggered case)

State Population (in thousands of persons) living below committed sea levels by scenario: median (white) and 17th–83rd percentile estimates (shaded)
RCP 2.6 through 2100 RCP 4.5 through 2100 RCP 6.0 through 2100 RCP 8.5 through 2100
Alaska 52 38–62 54 40–64 57 44–67 65 55–76
Alabama 63 37–91 68 41–96 76 49–108 100 71–149
California 1,947 1,249–2,652 2,070 1,382–2,776 2,282 1,595–2,990 2,904 2,197–3,602
Connecticut 194 113–275 208 125–289 228 145–309 284 203–363
District of Columbia 17 7–25 19 8–26 21 11–28 26 19–34
Delaware 92 53–145 100 59–155 112 68–171 154 99–220
Florida 8,654 6,209–10,206 9,014 6,633–10,443 9,502 7,336–10,777 10,595 9,253–11,458
Georgia 333 186–398 350 216–403 372 258–412 406 358–432
Hawaii 282 214–330 292 227–339 309 250–353 353 308–395
Louisiana 1,790 1,440–2,065 1,843 1,504–2,104 1,925 1,612–2,164 2,131 1,880–2,325
Massachusetts 650 464–818 677 497–846 717 543–887 832 664–1,004
Maryland 273 164–393 293 181–410 325 210–434 409 292–505
Maine 35 19–56 38 22–60 43 25–65 57 36–79
Mississippi 117 53–191 129 65–203 150 82–221 211 138–254
North Carolina 388 263–535 410 286–565 446 319–610 574 416–714
New Hampshire 17 11–24 18 12–25 20 13–27 24 17–32
New Jersey 1,003 685–1,296 1,054 741–1,342 1,130 822–1,416 1,332 1,044–1,635
New York 2,037 1,178–2,827 2,169 1,318–2,957 2,366 1,547–3,159 2,922 2,134–3,738
Oregon 42 27–55 45 30–58 48 34–65 61 46–80
Pennsylvania 117 43–211 129 53–231 150 71–261 227 127–339
Rhode Island 55 30–82 59 34–86 66 40–93 85 58–113
South Carolina 532 326–698 566 363–719 617 421–752 728 580–841
Texas 675 372–1,096 747 418–1,182 873 500–1,345 1,262 811–1,856
Virginia 1,200 744–1,399 1,248 858–1,416 1,316 1,001–1,444 1,418 1,254–1,538
Washington 167 121–207 174 130–215 185 144–230 220 178–278
  US total 20,734 14,048–26,138 21,775 15,242–27,010 23,338 17,142–28,387 27,379 22,240–32,061

Projections assume zero additional emissions after emissions end dates listed. The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. Levels of committed warming and SLR associated with each scenario are shown in Table S1. US totals include only the listed states and the District of Columbia.

Discussion

Our analysis makes a series of simplifying assumptions similar to those made in a previous commentary (41). One is a focus on warming driven only by carbon, ignoring short-lived climate pollutants, because of our emphasis on long-term commitment. Another is that, other than the carbon removal already incorporated in RCP 2.6, large-scale active withdrawal of carbon from the atmosphere via human efforts will not be feasible or effective. We leave out potential reductions in Atlantic Meridional Overturning Circulation, which could temporarily add ∼1 m of local sea level to East Coast locations at peak rates of Greenland melt (4244).

A fourth simplification is the use of arbitrary thresholds to define commitment for cities. Because the mean SLR combines with episodic storm-driven floods, some municipalities—e.g., in southern Florida, with its high risk of hurricanes and its porous bedrock—are unlikely to survive challenges lesser than the focal 50% cutoff, but others may be able to use measures such as levees to manage greater challenges. Tables S1 and S2 include tabulations at a 25% cutoff, which in most cases leads to roughly a quarter more city commitments than seen with the 50% cutoff, and at a 100% cutoff, which broadly reduces city commitments by well more than half.

In this century, many large cities that do not commit at 50% do lock in at 25% under various RCP scenarios. For the baseline case, the cities in this set with more than 300,000 residents are New York City; Boston; Long Beach, CA; Honolulu; Tampa, FL; and Corpus Christi, TX. In the same size category, 100% of New Orleans commits under RCP 6.0 or 8.5. Tables S3 and S4 list all cities with populations exceeding 100,000 that lock in under any baseline scenario at 25, 50, and 100% thresholds and detail critical cumulative emissions totals, sea-level increments, and lock-in years for each city. Tables S5 and S6 provide the same results for scenarios under the triggered assumption.

Table S4.

Cities exceeding 100,000 residents where 50 or 100% of the 2010 population-weighted area will fall below the future committed high tide line, making no assumption about WAIS collapse (baseline case)

City State Total population Population rank Critical cumulative emissions, GtC Committed SLR, m Commitment year
RCP 8.5 RCP 6.0 RCP 4.5 RCP 2.6
Commitment threshold: 50%
 Beaumont TX 118,286 22 2,210 6.6 2095
 Cambridge MA 105,162 25 940 2.8 2045 2055 2055
 Cape Coral FL 153,809 14 820 2.5 2035 2045 2040 2060
 Charleston SC 119,875 21 790 2.4 2035 2040 2040 2050
 Chesapeake VA 221,576 10 1,360 4.0 2065 2080
 Coral Springs FL 121,062 20 1040 3.1 2050 2060 2060
 Fort Lauderdale FL 165,521 12 AE 1.6 AE AE AE AE
 Hampton VA 137,373 17 1,000 2.9 2045 2060 2060
 Hialeah FL 224,634 9 AE 1.7 AE AE AE AE
 Hollywood FL 139,946 15 630 2.1 2025 2025 2025 2025
 Huntington Beach CA 189,992 11 1,160 3.4 2055 2070 2080
 Jacksonville FL 819,050 1 2,320 7.0 2100
 Metairie LA 138,481 16 AE 0.3 AE AE AE AE
 Miami FL 399,457 4 820 2.5 2035 2045 2040 2060
 Miami Gardens FL 107,167 24 570 1.8 2020 2020 2020 2020
 Miramar FL 107,278 23 AE 1.6 AE AE AE AE
 New Orleans LA 343,467 5 AE 0.3 AE AE AE AE
 Norfolk VA 242,751 8 980 2.9 2045 2060 2055
 Pembroke Pines FL 123,802 19 AE 1.6 AE AE AE AE
 Port St. Lucie FL 164,438 13 1,880 5.8 2085
 Sacramento CA 466,486 2 1,700 5.0 2075
 Savannah GA 136,286 18 1,650 4.9 2075 2100
 St. Petersburg FL 244,767 7 1,550 4.6 2070 2095
 Stockton CA 277,588 6 950 2.8 2045 2055 2055
 Virginia Beach VA 436,497 3 1,320 3.9 2060 2080
Commitment threshold: 100%
 Cape Coral FL 153,809 3 1,950 6.0 2085
 Hialeah FL 224,634 2 1,160 3.5 2055 2070 2080
 Hollywood FL 139,946 4 2,240 7.0 2095
 Metairie LA 138,481 5 1,210 3.5 2055 2075 2090
 Miami Gardens FL 107,167 8 1,790 5.5 2080
 Miramar FL 107,278 7 2,420 7.5 2100
 New Orleans LA 343,467 1 1,540 4.5 2070 2095
 Pembroke Pines FL 123,802 6 1,340 4.0 2065 2080

The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. Rows for the 10 largest cities are shaded underneath each commitment threshold level. See the legend of Table S3 for further documentation.

Table S5.

Cities exceeding 100,000 residents where 25% of the 2010 population-weighted area will fall below the future committed high tide line, assuming inevitable collapse of the WAIS under any emissions scenario (triggered case)

City State Total population Population rank Critical cumulative emissions, GtC Committed SLR, m Commitment year
RCP 8.5 RCP 6.0 RCP 4.5 RCP 2.6
Beaumont TX 118,286 39 1,310 5.4 2060 2080
Boston MA 617,594 3 AE 2.8 AE AE AE AE
Bridgeport CT 144,229 28 1,770 6.2 2080
Brownsville TX 175,023 22 2,050 6.9 2090
Cambridge MA 105,162 44 AE 1.5 AE AE AE AE
Cape Coral FL 153,809 25 AE 1.9 AE AE AE AE
Charleston SC 119,875 38 AE 1.6 AE AE AE AE
Chesapeake VA 221,576 17 AE 2.9 AE AE AE AE
Clearwater FL 107,685 40 1,600 6.0 2075 2095
Coral Springs FL 121,062 37 AE 2.8 AE AE AE AE
Corpus Christi TX 305,184 11 1,420 5.6 2065 2085
Elizabeth NJ 124,969 35 1,520 5.7 2070 2090
Elk Grove CA 152,772 26 1,380 5.5 2065 2085
Fort Lauderdale FL 165,521 23 AE 1.2 AE AE AE AE
Hampton VA 137,373 32 AE 2.7 AE AE AE AE
Hayward CA 142,760 29 1,860 6.5 2080
Hialeah FL 224,634 16 AE 1.5 AE AE AE AE
Hollywood FL 139,946 30 AE 1.5 AE AE AE AE
Honolulu (urban) HI 337,248 9 AE 3.9 AE AE AE AE
Huntington Beach CA 189,992 20 AE 1.1 AE AE AE AE
Jacksonville FL 819,050 2 770 5.1 2035 2040 2040 2045
Jersey City NJ 247,597 13 AE 3.7 AE AE AE AE
Long Beach CA 458,815 5 1,660 6.1 2075 2100
Metairie LA 138,481 31 AE 0.1 AE AE AE AE
Miami FL 399,457 7 AE 1.7 AE AE AE AE
Miami Gardens FL 107,167 42 AE 1.6 AE AE AE AE
Miramar FL 107,278 41 AE 1.2 AE AE AE AE
Mobile AL 195,111 19 2,400 7.6 2100
New Haven CT 129,779 34 2,210 7.2 2095
New Orleans LA 343,467 8 AE 0.2 AE AE AE AE
New York NY 8,175,083 1 1,890 6.5 2085
Newport News VA 180,659 21 1,770 6.3 2080
Norfolk VA 242,751 15 AE 2.7 AE AE AE AE
Oxnard CA 197,820 18 1,950 6.7 2085
Palm Bay FL 103,190 46 1,990 6.8 2085
Pasadena TX 149,043 27 2,420 7.7 2100
Pembroke Pines FL 123,802 36 AE 1.3 AE AE AE AE
Port St. Lucie FL 164,438 24 AE 4.6 AE AE AE AE
Richmond CA 103,668 45 2,220 7.4 2095
Sacramento CA 466,486 4 AE 3.2 AE AE AE AE
Savannah GA 136,286 33 AE 3.5 AE AE AE AE
St. Petersburg FL 244,767 14 AE 1.7 AE AE AE AE
Stockton CA 277,588 12 AE 1.4 AE AE AE AE
Tampa FL 335,654 10 AE 4.0 AE AE AE AE
Virginia Beach VA 436,497 6 AE 2.9 AE AE AE AE
Wilmington NC 106,476 43 1,830 6.4 2080

The years shown relate to emissions and associated commitments, not to the timing of ensuing warming or SLR. See the legend of Table S3 for further documentation.

Most of the municipalities included in this analysis are a great deal smaller than 100,000. As an illustration, the 1,596 cities committed at 50% under RCP 8.5 through 2100 under the triggered case have a mean population of 11,862 persons and a median population of 2,915 persons.

In a fifth simplification of this analysis, we restrict our scope to the United States. Clearly, the legacies of many more cities and nations, with less wealth to defend themselves, will be threatened globally. A recent study found that all of North America is home to ∼5% of the world’s coastal population living less than 10 m above sea level (45); accordingly, we address here only a small fraction of the overall challenge.

Sea-level threats to long-term cultural legacy are the main focus of this analysis. However, committed sea-level projections also may usefully inform nearer-term coastal and urban planning. For example, assuming RCP 2.6 to be a best-case scenario would give planners local estimates for minimum eventual SLR—a benchmark well above most 21st century projections, making explicit the transience of current needs. The implication is that measures aimed at lower amounts of SLR will suffice only for a limited time, suggesting the value of flexible approaches that can be extended in the future without prohibitive costs and continual rebuilding.

Nonetheless, a recent probabilistic assessment based on IPCC projections and expert elicitations on ice sheet behavior assigns a 0.5% chance that global SLR will exceed 6.3 m by 2200 under RCP 8.5 (46), suggesting that all but the highest committed levels discussed here could be attained in the relatively near term.

Summary and Conclusions

Cumulative carbon emissions lead to roughly proportional temperature increases expected to endure for millennia (6). These sustained increases translate to increments of SLR far exceeding the projections for this century, as ice sheets approach equilibrium with temperature over time (10). We find that within a 2,000-y envelope there is a strong relationship between cumulative emissions and committed sea level under either of our tested assumptions about WAIS stability, but the relationship is particularly steep when we do not assume collapse to be inevitable. In the latter case especially, rapid and deep cuts in carbon emissions could help many hundreds of coastal US municipalities avoid extreme future difficulties. However, historic carbon emissions appear already to have put in motion long-term SLR that will endanger the continuity and legacy of hundreds more municipalities, and so long as emissions continue, the tally will continually increase.

Acknowledgments

We thank Claudia Tebaldi for statistical advice; Stanley Jacobs for discussion of Southern Ocean circulation; Nathan Gillett for guidance on the transient climate response to emissions; Mark Merrifield for tidal modeling applied to the Alaskan coast; and Michael Oppenheimer for thoughtful comments on the manuscript. The research leading to these results received funding from the Kresge Foundation, the Rockefeller Foundation, the Schmidt Family Foundation, the V. Kann Rasmussen Foundation, and the European Union Seventh Framework Programme FP7/2007-2013 under Grant Agreement 603864.

Footnotes

The authors declare no conflict of interest.

This article is a PNAS Direct Submission.

This article contains supporting information online at www.pnas.org/lookup/suppl/doi:10.1073/pnas.1511186112/-/DCSupplemental.

References

  • 1.Field C, et al. Climate Change 2014: Impacts, Adaptation, and Vulnerability. Contribution of Working Group II to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge Univ Press; Cambridge, UK: 2014. [Google Scholar]
  • 2.Solomon S, Plattner G-K, Knutti R, Friedlingstein P. Irreversible climate change due to carbon dioxide emissions. Proc Natl Acad Sci USA. 2009;106(6):1704–1709. doi: 10.1073/pnas.0812721106. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Eby M, et al. Lifetime of anthropogenic climate change: Millennial time scales of potential CO2 and surface temperature perturbations. J Clim. 2009;22(10):2501–2511. [Google Scholar]
  • 4.Friedlingstein P, et al. Long-term climate implications of twenty-first century options for carbon dioxide emission mitigation. Nat Clim Chang. 2011;1(9):457–461. [Google Scholar]
  • 5.Zickfeld K, et al. Long-term climate change commitment and reversibility: An EMIC intercomparison. J Clim. 2013;26(16):5782–5809. [Google Scholar]
  • 6.Collins M, et al. In: Long-term Climate Change: Projections, Commitments and Irreversibility. Climate Change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Stocker TF, et al., editors. Cambridge Univ Press; Cambridge, UK: 2013. pp. 1029–1136. [Google Scholar]
  • 7.Dutton A, et al. Sea-level rise due to polar ice-sheet mass loss during past warm periods. Science. 2015;349(6244):aaa4019. doi: 10.1126/science.aaa4019. [DOI] [PubMed] [Google Scholar]
  • 8.Grant KM, et al. Rapid coupling between ice volume and polar temperature over the past 150,000 years. Nature. 2012;491(7426):744–747. doi: 10.1038/nature11593. [DOI] [PubMed] [Google Scholar]
  • 9.Abe-Ouchi A, et al. Insolation-driven 100,000-year glacial cycles and hysteresis of ice-sheet volume. Nature. 2013;500(7461):190–193. doi: 10.1038/nature12374. [DOI] [PubMed] [Google Scholar]
  • 10.Levermann A, et al. The multimillennial sea-level commitment of global warming. Proc Natl Acad Sci USA. 2013;110(34):13745–13750. doi: 10.1073/pnas.1219414110. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Stocker TF, et al. Climate Change 2013: The Physical Science basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge Univ Press; Cambridge, UK: 2013. [Google Scholar]
  • 12.Hinkel J, et al. Coastal flood damage and adaptation costs under 21st century sea-level rise. Proc Natl Acad Sci USA. 2014;111(9):3292–3297. doi: 10.1073/pnas.1222469111. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Marzeion B, Levermann A. Loss of cultural world heritage and currently inhabited places to sea-level rise. Environ Res Lett. 2014;9(3):034001. [Google Scholar]
  • 14.Shortridge A, Messina J. Spatial structure and landscape associations of SRTM error. Remote Sens Environ. 2011;115(6):1576–1587. [Google Scholar]
  • 15.Gesch DB. Analysis of lidar elevation data for improved identification and delineation of lands vulnerable to sea-level rise. J Coast Res. 2009;Special Issue 53:49–58. [Google Scholar]
  • 16.Strauss BH, Ziemlinski R, Weiss JL, Overpeck JT. Tidally adjusted estimates of topographic vulnerability to sea level rise and flooding for the contiguous United States. Environ Res Lett. 2012;7(1):014033. [Google Scholar]
  • 17.Favier L, et al. Retreat of Pine Island Glacier controlled by marine ice-sheet instability. Nat Clim Chang. 2014;5(2):1–5. [Google Scholar]
  • 18.Rignot E, Mouginot J, Morlighem M, Seroussi H, Scheuchl B. Widespread, rapid grounding line retreat of Pine Island, Thwaites, Smith, and Kohler glaciers, West Antarctica, from 1992 to 2011. Geophys Res Lett. 2014;41(10):3502–3509. [Google Scholar]
  • 19.Joughin I, Smith BE, Medley B. Marine ice sheet collapse potentially under way for the Thwaites Glacier Basin, West Antarctica. Science. 2014;344(6185):735–738. doi: 10.1126/science.1249055. [DOI] [PubMed] [Google Scholar]
  • 20.Gillett NP, Arora VK, Matthews D, Allen MR. Constraining the ratio of global warming to cumulative CO2 emissions using CMIP5 simulations. J Clim. 2013;26(18):6844–6858. [Google Scholar]
  • 21.Riahi K, Grübler A, Nakicenovic N. Scenarios of long-term socio-economic and environmental development under climate stabilization. Technol Forecast Soc Change. 2007;74(7):887–935. [Google Scholar]
  • 22.Peters G, Andrew R, Boden T, Canadell J. The challenge to keep global warming below 2 C. Nat Clim Chang. 2013;3(1):4–6. [Google Scholar]
  • 23.Raupach MR, et al. Sharing a quota on cumulative carbon emissions. Nat Clim Chang. 2014;4(10):873–879. [Google Scholar]
  • 24.US Energy Information Administration . Annual Energy Review 2011. USEIA; Washington, DC: 2012. [Google Scholar]
  • 25.Bamber JL, Riva REM, Vermeersen BL, LeBrocq AM. Reassessment of the potential sea-level rise from a collapse of the West Antarctic Ice Sheet. Science. 2009;324(5929):901–903. doi: 10.1126/science.1169335. [DOI] [PubMed] [Google Scholar]
  • 26.Weertman J. Stability of the junction of an ice sheet and an ice shelf. J Glaciol. 1974;13(67):3–11. [Google Scholar]
  • 27.Schoof C. Ice sheet grounding line dynamics: Steady states, stability, and hysteresis. J Geophys Res. 2007;112(F3):F03S28. [Google Scholar]
  • 28.Levermann A, et al. Potential climatic transitions with profound impact on Europe. Clim Change. 2011;110(3-4):845–878. [Google Scholar]
  • 29.Bamber JL, Aspinall WP. An expert judgement assessment of future sea level rise from the ice sheets. Nat Clim Chang. 2013;3(4):424–427. [Google Scholar]
  • 30.Jacobs SS, Jenkins A, Giulivi CF, Dutrieux P. Stronger ocean circulation and increased melting under Pine Island Glacier ice shelf. Nat Geosci. 2011;4(8):519–523. [Google Scholar]
  • 31.Thoma M, Jenkins A, Holland D, Jacobs S. Modelling Circumpolar Deep Water intrusions on the Amundsen Sea continental shelf, Antarctica. Geophys Res Lett. 2008;35(18):2–7. [Google Scholar]
  • 32.Jacobs S, et al. Getz Ice Shelf melting response to changes in ocean forcing. J Geophys Res Ocean. 2013;118(9):4152–4168. [Google Scholar]
  • 33.Dutrieux P, et al. Strong sensitivity of Pine Island ice shelf melting to climatic variability. Science. 2014;343(6167):174–178. doi: 10.1126/science.1244341. [DOI] [PubMed] [Google Scholar]
  • 34.Assmann KM, et al. Variability of circumpolar deep water transport onto the Amundsen Sea Continental shelf through a shelf break trough. J Geophys Res Ocean. 2013;118(12):6603–6620. [Google Scholar]
  • 35.Velicogna I, Sutterley TC, van den Broeke MR. Regional acceleration in ice mass loss from Greenland and Antarctica using GRACE time-variable gravity data. Geophys Res Lett. 2014;41(22):8130–8137. [Google Scholar]
  • 36.Mitrovica JX, Milne GA. On post-glacial sea level: I. General theory. Geophys J Int. 2003;154(2):253–267. [Google Scholar]
  • 37.Kendall RA, Mitrovica JX, Milne GA. On post-glacial sea level - II. Numerical formulation and comparative results on spherically symmetric models. Geophys J Int. 2005;161(3):679–706. [Google Scholar]
  • 38.Mitrovica JX, Wahr J, Matsuyama I, Paulson A. The rotational stability of an ice-age earth. Geophys J Int. 2005;161(2):491–506. [Google Scholar]
  • 39.Egbert GD, Erofeeva SY. Efficient inverse modeling of barotropic ocean tides. J Atmos Ocean Technol. 2002;19(2):183–204. [Google Scholar]
  • 40.Church JA, White NJ. A 20th century acceleration in global sea-level rise. Geophys Res Lett. 2006;33(1):L01602. [Google Scholar]
  • 41.Strauss BH. Rapid accumulation of committed sea-level rise from global warming. Proc Natl Acad Sci USA. 2013;110(34):13699–13700. doi: 10.1073/pnas.1312464110. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42.Levermann A, Griesel A, Hofmann M, Montoya M, Rahmstorf S. Dynamic sea level changes following changes in the thermohaline circulation. Clim Dyn. 2005;24(4):347–354. [Google Scholar]
  • 43.Yin J, Schlesinger ME, Stouffer RJ. Model projections of rapid sea-level rise on the northeast coast of the United States. Nat Geosci. 2009;2(4):262–266. [Google Scholar]
  • 44.Hu A, Meehl GA, Han W, Yin J. Effect of the potential melting of the Greenland Ice Sheet on the Meridional Overturning Circulation and global climate in the future. Deep Sea Research Part II Topical Studies in Oceanography. 2011;58(17–18):1914–1926. [Google Scholar]
  • 45.Lichter M, Vafeidis AT, Nicholls RJ, Kaiser G. Exploring data-related uncertainties in analyses of land area and population in the “Low-Elevation Coastal Zone” (LECZ) J Coast Res. 2011;27(4):757–768. [Google Scholar]
  • 46.Kopp RE, et al. Probabilistic 21st and 22nd century sea-level projections at a global network of tide-gauge sites. Earths Futur. 2014;2(8):383–406. [Google Scholar]

Articles from Proceedings of the National Academy of Sciences of the United States of America are provided here courtesy of National Academy of Sciences

RESOURCES