Future urban development exacerbates coastal exposure in the Mediterranean

Abstract

Changes in the spatial patterns and rate of urban development will be one of the main determinants of future coastal flood risk. Existing spatial projections of urban extent are, however, often available at coarse spatial resolutions, local geographical scales or for short time horizons, which limits their suitability for broad-scale coastal flood impact assessments. Here, we present a new set of spatially explicit projections of urban extent for ten countries in the Mediterranean, consistent with the Shared Socioeconomic Pathways (SSPs). To model plausible future urban development, we develop an Urban Change Model, which uses input variables such as elevation, population density or road network and an artificial neural network to project urban development on a regional scale. The developed future projections for the five SSPs indicate that accounting for the spatial patterns of urban development can lead to significant differences in the assessment of future coastal urban exposure. The increase in exposure in the Extended Low Elevation Coastal Zone (E-LECZ = area below 20 m of elevation) until 2100 can vary, by up to 104%, depending on the urban development scenario chosen. This finding highlights that accounting for urban development in long-term adaptation planning, e.g. in the form of land-use planning, can be an effective measure for reducing future coastal flood risk on a regional scale.

Introduction

The urban extent in low lying coastal areas is increasing faster than in other regions1, thus leading to increased exposure to sea-level rise and associated hazards. Societies' risk from these hazards will, therefore, not only depend on the physical drivers of change but also on the rate and pattern of urban growth which will be guided, to a large extent, by policies on future urban development2. One way to investigate how urban development influences future coastal flood risk is by accounting for spatiotemporal urban land cover change with the use of spatially explicit future urban projections in coastal impact assessments. Spatially explicit future urban extent scenarios are, however, currently often not available on a regional scale, which is one of the major shortcomings in coastal impact assessments to date3. Until recently, most studies have considered physical drivers of future change, partly accounting for population and economic development4 but have neglected changes in the spatial extent of urban agglomerations, where most impacts occur. Large scale urban change models can help to better understand how a non-climatic driver, namely urban development, influences future risk.

Different concepts and methods have been developed for modelling future urban change. Consequently, there now exists a vast diversity in modelling approaches, concepts, and models striving to describe and understand the mechanisms of land cover change. These approaches include, among others, the use of Cellular Automata5, Monte Carlo simulations6, Artificial Neural Networks7, as well as process-based and empirical models (e.g. CLUE)8. To date, most spatially explicit urban extent studies involve local applications2,7,9,10, and few broad-scale studies exist. Examples of regional-scale applications of urban change models include the studies of Seto et al.11, Zhou et al.12 and Gao and O'Neil13. Seto et al.11 used the land change model GEOMOD and a Monte Carlo simulation approach using projected GDP and urban population to develop spatially explicit probabilistic forecasts of urban land cover change until 2030 with a resolution of ~ 5 km. Zhou et al.12 used the SLEUTH Urban Growth model to develop urban land cover projections between 2012 and 2050 based on urban maps generated from LandScan population data at a resolution of 1 km. SLEUTH is an abbreviation that stands for all the inputs used in the model, which are slope, land cover, excluded regions, urban land cover, transportation and hill shade (Zhou et al. 2019). Recently, Gao and O'Neil13 developed an empirical model based on spatial data, the Spatially Explicit Long-term Empirical City developmenT (SELECT) model, to project urban land cover over the 21 century with a resolution of ~ 14 km. All the studies mentioned above are too coarse, in terms of spatial resolution, for regional coastal applications while in most cases the time horizon of the projections is too short for long-term coastal impact assessments.

In this paper, we address this gap by developing spatially explicit projections of urban extent for 10 Mediterranean countries with a resolution of 100 m, which is 10 to 140 times finer than existing gridded urban extent projections. For this purpose, we couple a Multilayer Perceptron (MLP) with a Geographic Information System to generate spatially explicit urban extent projections, for a range of socio-economic scenarios, until 2100. MLP is one of the modelling tools that has recently been used in the attempt to explore the complexity of interactions that govern the patterns in which urban extent changes and evolve14,15. An MLP has the ability to quantify complex behaviour and patterns16 by taking into account non-linear relationships between the input and output variables and generalise in the presence of noisy or incomplete data17.

Our projections are quantitatively and qualitatively consistent with the assumptions of the global Shared Socioeconomic Pathways (SSPs), which have been developed to support vulnerability and impact assessment studies. The SSPs comprise narratives that describe five different plausible pathways of societal development and also include information on future urban outcomes (see Table 1)18,19. In specific, urbanisation in SSP1 and SSP5 is rapid, although it is less well managed in SSP519, leading to higher urban sprawl. In SSP3 urbanisation proceeds slowly with mixed spatial patterns, particularly in developing countries, which are characterised by inequality and fragmentation. Urban settlements are poorly planned, and limited urban employment opportunities lead to unattractive urban centres and slow urbanisation rates in SSP3. However, population growth is rapid under SSP320 (except for the wealthier OECD countries) leading to high demand for urban space. A rapid urbanisation rate characterises SSP4 in medium and low-income countries, and central urbanisation rate in high-income countries with mixed spatial patterns, mainly driven by a lack of rural employment opportunities. Population growth is low in Mediterranean countries. SSP2 describes a world with a development that occurs at rates consistent with historical patterns of urbanisation and spatial patterns19.

Table 1 Summary of the Shared Socioeconomic Pathway assumptions underlying urban development (based on Jones and O'Neill19; Jiang and O'Neill18 and KC and Lutz20).

In a final step, we use the developed scenarios to investigate how coastal exposure changes in the future. We choose the Mediterranean region as it is considered a hotspot of urban development globally. Between 1960 and 2010, the urban population increased by 20%21. A large share of urban development takes place along the coast where most of the industry and services are located22. According to Seto et al.11, the region is expected to experience a 160% increase in urban extent between 2000 and 2030. Therefore, many Mediterranean cities will be potentially exposed to climate-related hazards such as coastal flooding and erosion. Even though the current level of risk is not high in the Mediterranean, it is likely to increase in the future23,24, also due to socio-economic development. Thus, the Mediterranean region can be considered as an adaptation hotspot25.

Results

Spatially explicit projections of urban extent

At the Mediterranean scale, we find substantial differences in future urban development rates and patterns until 2100 between the different projections (Figs. 1 and 2). The difference between the high and low urban extent projection ranges between 25% (HRV) and 115% (FRA) within the countries in the year 2100. Under all SSPs, urban extent increases during the century (Fig. 1). Until 2085, SSP5 produces the highest urban extent in all countries, reflecting the underlying narrative of a high urbanisation rate combined with urban sprawl. Interestingly, for some countries, the urban extent under SSP3 is, towards the end of the century, higher than under SSP5 (see Fig. 1—HRV and BIH). Rapid population growth in lower-income countries seems to be the main driver for urban land demand after 2085. SSP3 is characterised by a low fertility rate and declining population in most of the developed world20, leading to limited growth in urban extent in the wealthier European Mediterranean OECD countries (France, Greece, Italy, Slovenia, Spain) as well as in Turkey and Malta until 2100. In contrast, in the same scenario, the urban extent is highest in Bosnia-Herzegovina, Croatia, and Cyprus due to rapid population growth in those countries under SSP3. SSP5 shows the highest urban extent in wealthier European Mediterranean OECD countries and second highest in the rest of the countries (except for Malta). SSP5 is characterised by a high population growth driven by optimistic economic outlooks leading to a high GDP in high-income countries26. At the same time, in the rest of the countries, rapid development causes slower population growth compared to SSP319. SSP1 is characterised by fast urbanisation rates and concentrated spatial patterns18 in all countries but a relatively low population increase. This leads to the second-highest urban extent in the wealthier European Mediterranean OECD countries and Turkey. In contrast, the increase in urban extent is relatively low in Malta, Bosnia-Herzegovina, Cyprus, and Croatia, where the population seems to be the primary driver of future urban extent in 2100. In all countries (except for Malta) SSP2 represents a middle-of-the-road urban future with moderate urban development (Fig. 1 and Supplementary Table 1 and Supplementary Fig. 1).

Figure 1
figure1

Temporal development of urban extent for six selected countries from 2025 to 2100. Note that the scales on the y-axis are different for each graph (created with Python 3.7.4 using matplotlib, https://www.python.org/downloads/release/python-374/).

Figure 2
figure2

Spatially explicit urban extent in 2100 for different SSPs. European Mediterranean Countries included in the study are highlighted in darker shades of grey in the upper panel. For four selected regions, we present the spatially explicit urban extent scenarios that produce the highest and lowest urban extent. (Maps created with ArcGIS 10.6.1)

Ranking the SSPs according to their total urban extent in 2100 from lowest to highest (see Supplementary Table 2) shows that the wealthier European Mediterranean OECD countries follow the same patterns, with SSP3 having the smallest extent and SSP5 the highest. Bosnia-Herzegovina, Cyprus, and Croatia form a second group with similar patterns, this time with SSP4 having the lowest urban extent and SPP5 the highest, leading to up to 28% differences in the urban extent between the scenarios in 2100. Turkey and Malta seem to develop differently. Malta is highly urbanised, thus having the highest urban share of all countries (one-third of the nation is urban). The greatest urban extent for Malta occurs under SSP2, reflecting the historical pattern of urbanisation. Malta's high historical urban development rates combined with a high GDP under SSP2 lead to the highest urban extent. The high urban share in Malta leads to very few rural pixels that can convert in the future to urban. We investigated that the spatial allocation of future urban land may be plausible but somewhat unrealistic in Malta. We argue that such a high urban development rate in such a small country illustrates the challenges of urban land allocation in the future if urban development will be rapid and not well managed.

Future coastal urban exposure in 2100

Depending on the urban development scenario chosen the urban extent increases in the E-LECZ (area below 20 m) between 2012 and 2100, for instance, by 67% (2,075 km2) for Italy, 104% (2,331 km2) for France (Mediterranean coast only) and 86% (691 km2) for Greece (Fig. 3 and Supplementary Table 3).

Figure 3
figure3

Country-specific increase in urban extent in the E-LECZ between 2012 and 2100 [in km2] for the five SSPs (created with Python 3.7.4 using matplotlib, https://www.python.org/downloads/release/python-374/).

The urban extent scenario that leads to the highest urban exposure in the E-LECZ is the one that also produces the highest total urban extent in 2100 (see section "Spatially explicit projections of urban extent") reflecting that the model simulates high urban development in the E-LECZ. Figure 4 shows the spatial difference between 2012 and 2100 for four selected regions under SSP5. Compared to the year 2012, the urban extent increases in the floodplain in all regions leading to a significant increase in coastal exposure. Our results, therefore, show that accounting for the spatial patterns of coastal development can lead to significant differences in future exposure.

Figure 4
figure4

Potential urban development in four selected coastal regions under SSP5. In dark blue, the area that lies below 20 m is indicated (created with ArcGIS 10.6.1).

Discussion

The ability to project future urban development enables researchers and policymakers to better anticipate the consequences of specific actions, e.g. in the context of urban planning2, or to plan appropriate future inventions that can reduce exposure to future climate-related hazards such as coastal flooding. The spatially explicit urban extent scenarios offer, therefore, the possibility to analyse different urban futures and designate future priority areas for coastal adaptation in the Mediterranean. In this context, the results of this study can inform the development of future coastal management and adaptation policies on a regional scale27, such as those outlined in the Integrated Coastal Zone Management (ICZM) protocol of the Barcelona Convention28.

Our study shows that one of the most effective measures to reduce future exposure will be to reduce future urban development inside the coastal floodplain. The ICZM Protocol prescribes the implementation of a 100 m setback zone that restricts further development within this zone29. Spatial planning in the form of setback zones or even retreat can be one of the most effective interventions to reduce future exposure30 and lead to a more sustainable Mediterranean future urban development. However, coastal urban development could also entail positive effects to reduce future vulnerability to natural hazards and hence increase the overall adaptive capacity of cities31. Even if future urban exposure increases, the coastal vulnerability could decrease if actual adaptation action (e.g. in the form of hard protection) and disaster management are effectively implemented. Hence, we argue that the concentration of people and assets could also increase the efficiency and effectiveness of adaptation measures in the future. Future urban extent scenarios could be useful to explore these avenues and inform adaptation and spatial planning authorities what mix of adaptation strategies for different regions could be most effective.

Several studies of European cities had shown that even when population decreased urban extent increased32,33. This trend is also reflected in our developed spatially explicit urban extent scenarios, where urban extent increases with time under all scenarios, albeit at lower rates in those cases where population declines. The urban projections reflect that urban development is linked to GDP growth in high-income countries. In contrast, in lower-income countries, urban development is more driven by population growth towards the end of the century. This pattern has also been reported in other studies (e.g. see meta-analysis of global urban land expansion from Seto et al. 20111).

Model performance and limitations

Evaluating our country-specific urban change models against historical data indicates that these are capable of reproducing historical spatial patterns of urban development on a regional scale. We observed that the models of those countries with a high urban share and/or uniform urban sprawl patterns (see Table 2), such as Croatia, Slovenia, France or Cyprus, perform best. This indicates that the MLP model can better generalise on countries where a large enough sample of urban change is provided. As the extent of urban areas is small in comparison to that of rural areas, we have an imbalanced dataset due to an uneven distribution of classes (much more rural pixel, than urban). This poses a challenge from a Machine Learning perspective since models are harder to train with imbalanced training sets. This issue has been tackled by under-sampling the majority that is the rural class in our case, to create a more balanced training set. For most countries, the model performed best with an under-sampling ratio of 10 (1:10, Urban: Rural) (the undersampling ratio used for every country can be found in Supplementary Table 4). Further, we improved the performance of the MLP model by using data augmenting which creates additional training data. At the same time, the MLP is challenged when trying to reproduce inhomogeneous settlements, where urban development is fragmented with clustered and contrasted patterns. Such an example is Spain, where the performance of the MLP was the lowest (Table 2).

Table 2 Performance measures of the MLP for predicting urban extent in 2012 for every country.

The explanatory potential of the input variables was analysed by using entropy and mutual information34. Mutual information measures the dependencies between each feature and the output. It quantifies the information content of two variables in classification problems by considering the input–output statistics without any reference to a specific model. Mutual information should be interpreted relative to the entropy. The mathematical explanations of the two metrics can be found in the supplementary material. Supplementary Table 5 shows the mutual information and entropy values for every input variables and country. High mutual information means that the input feature is suitable in explaining the output. In nearly all countries, distance to urban land cover and the population density have the highest mutual information, reflecting the fact that new urban development is expected to grow near existing urban agglomerations. However, the order of magnitude between the variables is often similar, thus we believe that all input variables are useful for our MLP (see Supplementary Table 6). The entropy of a country can be interpreted as a measure of urbanisation in this study. In countries where the distribution of urban and rural pixels is more balanced (e.g. MLT 29% Urban; 70% Rural), the entropy is high (for MLT 0.8).

We must note that the validation measure' overall accuracy' along does not necessarily mean that the urban change model has high predictive power. Pontius and Malanson35 discuss several reasons why 'percent correct' alone is not enough to validate a model. Importantly, they state that a null model that predicts pure persistence between two-time steps often leads to more than 90% correct due to the temporal autocorrelation between the time steps. Additionally, the merit is not appropriate for imbalanced datasets36. Therefore, it is essential to consider the f1-score, precision, recall and a visual assessment of the spatial performance of the urban change model to assess the performance.

Future research could improve and extend this work in a number of ways. First, in our study, we assume a constant pattern of the input variables throughout the century due to lack of data. Hence, one central assumption of the study is that similar processes drive future urban development. For instance, urban development will change as a response to a changing road network but information on the future development of the road network is currently not available for most countries. The MLP model would be able to incorporate such processes if input data for all variables become available in the future, which would allow us to dynamically model future urban expansion from one time step to another. Second, the developed urban change model only considers spatial aspects and does not account for non-spatial elements such as demographic characteristics, spatial planning policies or tipping points that are unpredictable (such as natural hazards) which is a major challenge in urban land change models16. Future work could further expand the urban scenarios by accounting for policy interventions such as coastal adaptation measures in the form of setback zones that restricts future urban development in flood-prone areas or include vertical growth of cities into the scenarios. Last, a time interval of more than 12 years between the input and target data could lead to improved training of the MLP by providing a larger number of urban pixels that change from one time step to another. However, the lack of a consistent land cover time series with a high resolution that can be used as input (e.g. distance to forest, grassland) and output data (urban) to train the MLP is currently not available at this scale.

Conclusion

Urban growth rates and spatial patterns of urban development will determine society's exposure and vulnerability to extreme events, sea level, and other climate-related hazards. Urban development is a dynamic and complex process37 that is influenced by physical, socio-economic and political conditions. Hence, how urban development influences future risk has not yet been quantified and is not well understood2. Spatiotemporal land cover analysis and future urban land cover projections can help improve our understanding of these processes.

We have produced urban extent projections that cover a plausible range of uncertainty with a resolution of 100 m, spanning from 2025 to 2100. The developed urban projections are based on the global SSPs and thus depict five different plausible urban development scenarios. Across all SSPs, we observe a continued increase in urban areas in the coastal zone, which leads to an increase in coastal exposure, even though the rates and spatial patterns of urban development vary between the different scenarios. We anticipate that the developed urban extent scenarios will be employed in a wide range of impact assessments to climate change-related hazards beyond coastal applications.

Methods

To model plausible future urban extent, we developed a set of country-specific urban change models (see Fig. 5) as the rate and pattern of urban development can vary considerably across countries and years38. First, we employ an MLP artificial neural network for modelling the likelihood of urban transformation (see Fig. 5a). In a second step, we calculate, for each SSP, the future urban land demand in 5-year time steps until 2100 (see Fig. 5b). Finally, we create the urban extent scenarios by classifying the MLP model outputs accordingly (see Fig. 5c). These projections are then employed for calculating future exposure to coastal flooding (section “Future coastal flood exposure”).

Figure 5
figure5

Workflow of the urban change model (created using Photoshop CS4).

Urban change model

Step a: Likelihood of urban transformation

We used an MLP to generate a predictive spatially explicit model of urban development for 10 Mediterranean countries where data were available (MLT, CYP, GRC, SVN, ITA, BIH, HRV, FRA, ESP, TUR). An MLP is a computational model often used for complex, non-linear behavior, and patterns of unknown input–output relations7,39. Every MLP is composed of one input layer, one or several hidden layers, and one output layer. For a detailed description of MLPs see reference34.

The MLP was trained using input data from 2000 to reproduce CORINE urban land cover data from 2012 (https://land.copernicus.eu/). In this study, we define urban areas as locations dominated by artificial surfaces, which corresponds to the artificial surface class (code 1) from CORINE that includes residential, industrial, commercial, transport and green urban areas.

The input layer of our MLP consists of nine input variables (Table 3). The input variables have been selected based on literature review and data availability. Elevation and slope have been selected to reflect the topography, which influences urban development as steep areas, and areas of high elevation are less likely to develop7. Distance to roads has been included because areas that are easy to access are more likely of being developed40 as it is correlated to people's mobility7, which influences where people decide to settle. As the study focuses mainly on the exposure of urban areas to sea-level rise and climate-related hazards such as storm surges, we decided to also include the distance to the coast as an input variable. Low elevation coastal zones are developing faster than the hinterland38 and therefore distance to the coast can be an important predictor. We also included the Euclidian distance to urban areas, arable land, grassland, and forest to account for the effect of other types of land use on urban development. Finally, we used population density as an input variable to reflect socio-economic driving forces, as numerous studies show that these constitute underlying drivers of urban development.

Table 3 Summary of data used for input and output variables of the MLP.

The output layer consists of a single variable giving the likelihood that a pixel will turn urban in the next time step. To define the best MLP architecture for every country (i.e. the number of neurons in each layer, the connection patterns between the layers, the activation function and the learning methods) we conducted a sensitivity analysis using between 6 and 10 different network architectures. An overview of the best model architecture per country can be found in Supplementary Table 4.

Step b: Future urban land demand

In the second step, we calculated the future urban land demand for every country, SSP and time step. For this purpose, we used the relative changes in total urban extent for every country between 2020 and 2100, obtained from Li et al.38. This study developed (non-spatial) country‐specific urban extent growth models using data from an urban extent time series, spanning from 1992 to 2013 (22 years) based on satellite observations, and historical socio-economic indicators, namely Population and GDP. These country-specific models were then used to project future urban growth under the Shared Socioeconomic Pathways until the end of the twenty-first century using the population and GDP data from the SSP database. The reported mean accuracy for Europe compared to fine resolution land cover data was 95%38. In our model, we used the relative changes of Li et al. 2019 to calculate the total number of future urban grid cells.

Step c: Spatial classification

Finally, the future urban land demand per time step was used to reclassify our MLP outputs. The highest urban transformation likelihoods were reclassified according to the total number of future urban grid cells (see Fig. 5). We used CORINE 2012 as a starting year to create high-resolution spatially explicit urban extent scenarios that are consistent with the global SSP assumptions, in 5-year time steps until 2100. We produced scenarios for 10 European Mediterranean countries where global SSP assumption and CORINE data exist.

Future coastal flood exposure

Using the spatially explicit urban extent projections, we then assessed future coastal exposure for the Mediterranean coast in 2100. For this purpose, we calculated the low-lying part of the coastal zone that is hydrologically connected to the sea and lies above 20 m of mean sea level (E-LECZ). We decided to use the E-LECZ to account for all plausible future changes in mean sea level and associated extreme water levels41. The exposed area was overlaid with the developed urban extent projections to analyse the exposure of future urban extent for all SSPs.

MLP performance

We used a confusion matrix to evaluate the model performance (see Fig. 6) and find the MLP model architecture that best approximates the input–output relationships. The confusion matrix is a way to investigate the percentage of correct and incorrect classified pixels and is a measure for analysing the goodness of fit for a specific classification model architecture. The overall accuracy reflects the overall correct classified pixels. However, this metric is very sensitive to imbalanced datasets and can be misleading when measuring the MLP performance36 as our dataset contains few urban pixels compared to the rural class. A more appropriate merit to assess the performance of binary classification problems with a skewed dataset is, therefore, the F1-score. The F1 score is used to represent the balance between precision (Positive predictive value—the percentage of pixels that are classified as urban and are, in reality, urban) and recall (True positive rate—the ratio of the pixels that are correctly classified in relation to the total positive (target) pixels). It can be viewed as the harmonic mean of precision and recall. The results per country are presented in Table 2.

Figure 6
figure6

Confusion matrix (created using Photoshop CS4).

The urban change models can reproduce the observed patterns of past urban development between 2000 and 2012 with an F1-score between 68 and 99% in all countries (see Table 2). This indicates that the country-specific urban change models capture past patterns of urban development. However, the confusion matrix is not very useful in assessing spatial patterns. For instance, if a pixel is misclassified, regardless of whether the correct class is found in a neighbouring pixel, it is presented as incorrect35. Therefore, a visual assessment was conducted by overlaying the simulated and CORINE 2012 maps using a Geographic Information System to explore the spatial and qualitative patterns of the predicted model outputs (see Supplementary Fig. 2 for an example).

Data availability

The urban extent projections are available at the figshare repository (https://figshare.com/s/8fc878cbf3597c6574e1). Further, we provide the python code to set up the MLP model and create the urban extent projection in the figshare repository.

References

  1. 1.

    Seto, K. C., Fragkias, M., Guneralp, B. & Reilly, M. K. A meta-analysis of global urban land expansion. PLoS ONE 6, e23777. https://doi.org/10.1371/journal.pone.0023777 (2011).

    ADS  CAS  Article  PubMed  PubMed Central  Google Scholar 

  2. 2.

    Song, J., Fu, X., Wang, R., Peng, Z.-R. & Gu, Z. Does planned retreat matter? Investigating land use change under the impacts of flooding induced by sea level rise. Mitig. Adapt. Strat. Glob. Change 23, 703–733. https://doi.org/10.1007/s11027-017-9756-x (2017).

    Article  Google Scholar 

  3. 3.

    Muis, S., Guneralp, B., Jongman, B., Aerts, J. C. & Ward, P. J. Flood risk and adaptation strategies under climate change and urban expansion: a probabilistic analysis using global data. Sci. Total Environ. 538, 445–457. https://doi.org/10.1016/j.scitotenv.2015.08.068 (2015).

    ADS  CAS  Article  PubMed  Google Scholar 

  4. 4.

    Vousdoukas, M. I. et al. Economic motivation for raising coastal flood defenses in Europe. Nat. Commun. 11, 2119. https://doi.org/10.1038/s41467-020-15665-3 (2020).

    ADS  CAS  Article  PubMed  PubMed Central  Google Scholar 

  5. 5.

    Feng, Y., Liu, Y., Tong, X., Liu, M. & Deng, S. Modeling dynamic urban growth using cellular automata and particle swarm optimisation rules. Landscape Urban Plan. 102, 188–196. https://doi.org/10.1016/j.landurbplan.2011.04.004 (2011).

    Article  Google Scholar 

  6. 6.

    Güneralp, B. & Seto, K. C. Futures of global urban expansion: uncertainties and implications for biodiversity conservation. Environ. Res. Lett. https://doi.org/10.1088/1748-9326/8/1/014025 (2013).

    Article  Google Scholar 

  7. 7.

    Iizuka, K. et al. Modeling future urban sprawl and landscape change in the Laguna de Bay Area, Philippines. Land. https://doi.org/10.3390/land6020026 (2017).

    Article  Google Scholar 

  8. 8.

    8Verburg, P. H. & Overmars, K. P. in Modelling Land-Use Change: Progress and Applications (eds Eric Koomen, John Stillwell, Aldrik Bakema, & Henk J. Scholten) 321–337 (Springer, Dordrecht, 2007).

  9. 9.

    Pijanowski, B. C. et al. A big data urban growth simulation at a national scale: configuring the GIS and neural network based Land transformation model to run in a high performance computing (HPC) environment. Environ. Model. Softw. 51, 250–268. https://doi.org/10.1016/j.envsoft.2013.09.015 (2014).

    Article  Google Scholar 

  10. 10.

    Pijanowski, B. C., Shellito, B., Pithadia, S. & Alexandridis, K. Forecasting and assessing the impact of urban sprawl in coastal watersheds along eastern Lake Michigan. Lakes Reserv. Res. Manag. 7, 271–285. https://doi.org/10.1046/j.1440-1770.2002.00203.x (2002).

    Article  Google Scholar 

  11. 11.

    Seto, K. C., Guneralp, B. & Hutyra, L. R. Global forecasts of urban expansion to 2030 and direct impacts on biodiversity and carbon pools. Proc. Natl. Acad. Sci. USA 109, 16083–16088. https://doi.org/10.1073/pnas.1211658109 (2012).

    ADS  Article  PubMed  Google Scholar 

  12. 12.

    Zhou, Y., Varquez, A. C. G. & Kanda, M. High-resolution global urban growth projection based on multiple applications of the SLEUTH urban growth model. Sci. Data 6, 34. https://doi.org/10.1038/s41597-019-0048-z (2019).

    Article  PubMed  PubMed Central  Google Scholar 

  13. 13.

    Gao, J. & O’Neill, B. C. Mapping global urban land for the 21st century with data-driven simulations and Shared Socioeconomic Pathways. Nat. Commun. 11, 2302. https://doi.org/10.1038/s41467-020-15788-7 (2020).

    ADS  CAS  Article  PubMed  PubMed Central  Google Scholar 

  14. 14.

    Basse, R. M., Omrani, H., Charif, O., Gerber, P. & Bódis, K. Land use changes modelling using advanced methods: cellular automata and artificial neural networks. The spatial and explicit representation of land cover dynamics at the cross-border region scale. Appl. Geogr. 53, 160–171. https://doi.org/10.1016/j.apgeog.2014.06.016 (2014).

    Article  Google Scholar 

  15. 15.

    Chen, G. et al. Global projections of future urban land expansion under shared socioeconomic pathways. Nat. Commun. 11, 537. https://doi.org/10.1038/s41467-020-14386-x (2020).

    ADS  CAS  Article  PubMed  PubMed Central  Google Scholar 

  16. 16.

    Pijanowski, B. C., Brown, D. G., Shellito, B. A. & Manik, G. A. Using neural networks and GIS to forecast land use changes: a Land Transformation Model. Comput. Environ. Urban Syst. 26, 553–575. https://doi.org/10.1016/s0198-9715(01)00015-1 (2002).

    Article  Google Scholar 

  17. 17.

    Mas, J. F. & Flores, J. J. The application of artificial neural networks to the analysis of remotely sensed data. Int. J. Remote Sens. 29, 617–663. https://doi.org/10.1080/01431160701352154 (2008).

    ADS  Article  Google Scholar 

  18. 18.

    Jiang, L. & O’Neill, B. C. Global urbanisation projections for the shared socioeconomic pathways. Glob. Environ. Change 42, 193–199. https://doi.org/10.1016/j.gloenvcha.2015.03.008 (2017).

    Article  Google Scholar 

  19. 19.

    Jones, B. & O’Neill, B. C. Spatially explicit global population scenarios consistent with the Shared Socioeconomic Pathways. Environ. Res. Lett. https://doi.org/10.1088/1748-9326/11/8/084003 (2016).

    Article  Google Scholar 

  20. 20.

    Kc, S. & Lutz, W. The human core of the shared socioeconomic pathways: Population scenarios by age, sex and level of education for all countries to 2100. Glob. Environ. Change. https://doi.org/10.1016/j.gloenvcha.2014.06.004 (2014).

    Article  Google Scholar 

  21. 21.

    UNEP/MAP. Mediterranean Strategy for Sustainable Development 2016–2025 (Plan Bleu, Regional Activity Centre, Valbonne, 2016).

  22. 22.

    European Environment Agency. Horizon 2020 mediterranean report. (2014).

  23. 23.

    Cramer, W. et al. Climate change and interconnected risks to sustainable development in the Mediterranean. Nat. Clim. Change 8, 972–980. https://doi.org/10.1038/s41558-018-0299-2 (2018).

    ADS  Article  Google Scholar 

  24. 24.

    Reimann, L., Vafeidis, A. T., Brown, S., Hinkel, J. & Tol, R. S. J. Mediterranean UNESCO World Heritage at risk from coastal flooding and erosion due to sea-level rise. Nat. Commun. 9, 4161. https://doi.org/10.1038/s41467-018-06645-9 (2018).

    ADS  CAS  Article  PubMed  PubMed Central  Google Scholar 

  25. 25.

    Hallegatte, S., Green, C., Nicholls, R. J. & Corfee-Morlot, J. Future flood losses in major coastal cities. Nat. Clim. Change 3, 802–806. https://doi.org/10.1038/nclimate1979 (2013).

    ADS  Article  Google Scholar 

  26. 26.

    O’Neill, B. C. et al. The roads ahead: narratives for shared socioeconomic pathways describing world futures in the 21st century. Glob. Environ. Change 42, 169–180. https://doi.org/10.1016/j.gloenvcha.2015.01.004 (2017).

    Article  Google Scholar 

  27. 27.

    Haasnoot, M. et al. Generic adaptation pathways for coastal archetypes under uncertain sea-level rise. Environ. Res. Commun. 1, 071006. https://doi.org/10.1088/2515-7620/ab1871 (2019).

    Article  Google Scholar 

  28. 28.

    UNEP/MAP/PAP. Protocol on Integrated Coastal Zone Management in the Mediterranean (Priority Actions Programme Regional Activity Centre, Split, 2008).

  29. 29.

    Rochette, J., du Puy-Montbrun, G., Wemaëre, M. & Billé, R. Coastal setback zones in the Mediterranean: A study on Article 8-2 of the Mediterranean ICZM Protocol. (IDDRI, 2010).

  30. 30.

    Lincke, D. et al. The effectiveness of setback zones for adapting to sea-level rise in Croatia. Reg. Environ .Change 20, 46. https://doi.org/10.1007/s10113-020-01628-3 (2020).

    Article  Google Scholar 

  31. 31.

    Garschagen, M. & Romero-Lankao, P. Exploring the relationships between urbanisation trends and climate change vulnerability. Clim. Change 133, 37–52. https://doi.org/10.1007/s10584-013-0812-6 (2013).

    ADS  Article  Google Scholar 

  32. 32.

    Kasanko, M. et al. Are European cities becoming dispersed?. Landscape Urban Plan. 77, 111–130. https://doi.org/10.1016/j.landurbplan.2005.02.003 (2006).

    Article  Google Scholar 

  33. 33.

    Barranco, R. R., Silva, F. B. E., Marin Herrera, M. & Lavalle, C. Integrating the MOLAND and the Urban Atlas Geo-databases to analyse urban growth in European Cities. J. Map Geogr. Libr. 10, 305–328. https://doi.org/10.1080/15420353.2014.952485 (2014).

    Article  Google Scholar 

  34. 34.

    Theodoridis, S. Machine Learning: A Bayesian and Optimisation Perspective (Academic Press Inc., London, 2015).

    Google Scholar 

  35. 35.

    Pontius, G. R. & Malanson, J. Comparison of the structure and accuracy of two land change models. Int. J. Geogr. Inf. Sci. 19, 243–265. https://doi.org/10.1080/13658810410001713434 (2005).

    Article  Google Scholar 

  36. 36.

    Jeni, L. A., Cohn, J. F. & De La Torre, F. Facing imbalanced data recommendations for the use of performance metrics. Int. Conf. Affect Comput. Intell. Interact. Works. https://doi.org/10.1109/ACII.2013.47 (2013).

    Article  Google Scholar 

  37. 37.

    Schneider, A. et al. A new urban landscape in East-Southeast Asia, 2000–2010. Environ. Res. Lett. https://doi.org/10.1088/1748-9326/10/3/034002 (2015).

    Article  Google Scholar 

  38. 38.

    Li, X., Zhou, Y., Eom, J., Yu, S. & Asrar, G. R. Projecting global urban area growth through 2100 based on historical time series data and future shared socioeconomic pathways. Earth’s Future 7, 351–362. https://doi.org/10.1029/2019ef001152 (2019).

    ADS  Article  Google Scholar 

  39. 39.

    Pijanowski, B. C., Tayyebi, A., Delavar, M. R. & Yazdanpanah, M. J. Urban expansion simulation using geospatial information system and artificial neural networks. Int. J. Environ. Res. 3, 493–502. https://doi.org/10.22059/ijer.2010.64 (2009).

    Article  Google Scholar 

  40. 40.

    Tayyebi, A., Pijanowski, B. C. & Tayyebi, A. H. An urban growth boundary model using neural networks, GIS and radial parameterisation: An application to Tehran, Iran. Landscape Urban Plan. 100, 35–44. https://doi.org/10.1016/j.landurbplan.2010.10.007 (2011).

    Article  Google Scholar 

  41. 41.

    Wolff, C. et al. A Mediterranean coastal database for assessing the impacts of sea-level rise and associated hazards. Sci. Data 5, 11. https://doi.org/10.1038/sdata.2018.44 (2018).

    Article  Google Scholar 

Download references

Acknowledgements

We thank George Vafeidis for useful discussions on the use of ANNs and under-sampling. Open access funding provided by Projekt DEAL.

Author information

Affiliations

Authors

Contributions

C.W. conceived the initial idea of the study with input from A.T.V.; C.W., A.T.V., and T.N. designed research; C.W. and T.N. performed the analyses, created the scenarios and developed the code; all authors evaluated the results; C.W. wrote the first draft of the paper. T.N., A.T.V., and J.H. co-wrote the paper.

Corresponding author

Correspondence to Claudia Wolff.

Ethics declarations

Competing interests

The authors declare no competing interests.

Additional information

Publisher's note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Supplementary information

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Wolff, C., Nikoletopoulos, T., Hinkel, J. et al. Future urban development exacerbates coastal exposure in the Mediterranean. Sci Rep 10, 14420 (2020). https://doi.org/10.1038/s41598-020-70928-9

Download citation

Further reading

Comments

By submitting a comment you agree to abide by our Terms and Community Guidelines. If you find something abusive or that does not comply with our terms or guidelines please flag it as inappropriate.

Search

Quick links

Nature Briefing

Sign up for the Nature Briefing newsletter — what matters in science, free to your inbox daily.

Get the most important science stories of the day, free in your inbox. Sign up for Nature Briefing