Crop Sustainability and Five Domains in Mediterranean Region: Comparison
Please note this is a comparison between Version 2 by Peter Tang and Version 1 by Zulfa Hanan Ash’aari.

Most of the Mediterranean region has experienced frequent natural disasters, expanding population, increase in temperature, and increase in the surface of the Mediterranean Sea. Furthermore, the temperature in the Mediterranean area is rising 25% faster than the rest of the globe, and in the summer, it is warming 40% faster than the global average. Climate change can alter the food supply, restrict access to food, and degrade food quality. Temperature rises, changes in precipitation patterns, changes in severe weather events, and decreased water availability, for example, might all result in lower agricultural production. The fact that most Mediterranean nations rely on imported basic foodstuffs adds to the severity of the situation. Instability and insecurity of agricultural supply in the region might lead to massive population movement, transforming most Mediterranean nations into a global source of instability.

  • climate change
  • ecosystem
  • crop production
  • modelling
  • Mediterranean region

1. Introduction

The Mediterranean is the consequence of rifting, spreading, subduction, and colliding plates and microplates dating back to the Mesozoic [1]. After the Eocene, the African and Eurasian plates, and microplates like the Adria and Anatolia, the Tethys was formed, which became the proto-Mediterranean. Two eastern basins, the Paratethys, progressively split apart after this catastrophe [2]. The Sicily Channel separates the Western Mediterranean from the Eastern Mediterranean.
Historically, the Mediterranean served as significant trade and cultural exchange route between Europe, North Africa, the Middle East, and Asia. This was contributed by the rise of the Ottoman Empire, which emphasized the development of a network of sea routes to reach the countries of North Africa easily. The second is the Suez Canal, which linked the Indian Ocean and the Mediterranean and rekindled some trade between Asian and Mediterranean countries [3]. The Mediterranean region is depicted in Figure 1. The region is in a transition zone between the circulation patterns of mid-latitude and subtropical air. It has a complicated shape with mountain chains and significant differences between land and sea [4].
Figure 1.
Mediterranean countries. Source:
(accessed on 9 September 2022).

2. Effects of Climate Change on Agriculture in the Mediterranean Region

Mediterranean climatic is very similar to any of the following regions across the globe: California (United States); Central Chile; Cape Region (South Africa); and the southernmost regions (Australia) [called Mediterranean climatic regions (MCRs)]. The five regions constitute 2% of the Earth’s surface area, 20% of the world’s plant species, and 5% of the world’s population. However, just 6% of land in California is utilized for agriculture, whereas 37% of land in Australia and 55% in Chile’s central valley are used for agriculture [40][5]. Climate change increases the likelihood of drought and high heat, which is detrimental to agriculture in MCRs [41][6]. In semiarid regions, variable water supplies make it difficult to cultivate crops and have substantial social and economic consequences [42][7]. To make MCR less susceptible to CC, adjustments must be made to crops (such as annual crops, vegetables, orchards, and vineyards), cropping systems (the sequence of crops and management strategies employed on a particular farm area), and farming systems. Adaptation is altering the environment and its present or anticipated consequences to mitigate or prevent adverse effects and take advantage of positive ones. Numerous technical methods assist crops and agricultural systems to adapt to climate change. A deep understanding of the role of technology in adaptation requires the examination of how technology is used for extension and training [43][8]. Many rainfalls characterize MCRs in a short time during the year. Furthermore, rainfall in MCRs changes a lot from year to year and from month to month as a result of climate oscillations [44][9]. In addition to the above characteristics, the temperatures have gone up and rainfall has gone down in MCRs over the past 100 years due to CC [45][10]. The prediction models of MCRs by the end of the 21st century have shown that MCRs will have even less rain and warmer temperatures [46][11]. Another study suggested that rain is less often in the winter in MCRs, but in some places, it would rain more heavily [42][7]. Changes in how much and where it rains, along with high evaporation and transpiration (loss of water vapor through the stomata of plants) in the spring and summer, will cause the MCRs to lose more water over time. Hence, the effect of water and temperature on agriculture will be discussed in the next two sub-sections.

2.1. Effects of Water

Drought stress significantly impacts agricultural productivity [47][12]. Annual crops, such as cereals, are susceptible to progressive water scarcity during the blossoming and grain-filling phases in rainfed parts of the MCRs and semi-arid tropics, resulting in “terminal drought stress” [48][13]. During certain phenological times, a lack of water hinders leaf photosynthesis. The creation of photosynthetic was carried directly to the grain [49][14]. Consequently, the number of grains per spike/pod and grain weight is lowered significantly, resulting in lower grain yields [50][15]. The harvest index, or the proportion of aboveground biomass allocated to grain, decreases during terminal drought circumstances [51][16]. Photosynthesis provides activities to restore reserves during pre- and/or post-anthesis stages [41,52][6][17]. As a result, when leaf photosynthetic activity diminishes under terminal drought stress, the contribution of stem reserves (mostly water-soluble carbohydrates; WSCs) to grain is critical [48][13].
The quantity of water available for irrigation in most irrigated MCRs is decreasing due to recurring drought and intense competition for water resources among agriculture, industry, and urban areas. Higher temperatures, on the other hand, increase evapotranspiration and agricultural irrigation needs [53][18]. As a result, the objective is to reduce irrigation water use and its negative influence on seed/fruit yield and quality. It is well known that the influence of water scarcity on seed/fruit yield and quality varies greatly depending on the crop development stage. Water scarcity impacts the reproductive and seed/fruit development phases more than the vegetative or maturity stages. Water scarcity during the silking-pollination and blister periods of maize, for example, reduces seed set. It enhances grain abortion, leading to significant output losses [54][19]. In general, water shortages throughout the blooming and fruit development periods result in a more significant decline in fruit yield than shortfalls towards fruit maturity [55][20].

2.2. Effect of Temperature

MCR temperatures are anticipated to climb by 2–4 °C by the mid-twenty-first century [56][21]. High temperatures can affect various physiological and metabolic processes in plants, affecting their development, growth, and production. Higher temperatures related to CC have been shown to impair agricultural output and quality [57][22]. Even mild temperature increases hasten plant growth, shortening the growing season and decreasing plant biomass. Consequently, changes in phenological dates will change the crop season duration and water requirements. Temperatures and evaporation-spiration will rise in areas with warm spring and summer seasons (severe scenario, up to 4 °C) [58][23]. Warmer weather (moderate scenario, up to 2 °C) may benefit agricultural production when temperature restricts the duration of the growing season [33][24].

3. Sustainability and the Five Domains

The climate change in the Mediterranean Basin rates may outperform world trends for most variables, including rising temperatures, rainfall, and desertification, with annual mean temperatures currently 1.4 °C above levels from the late nineteenth century. Since 1950, it has been proven that heat waves and severe droughts have increased in frequency [21][25]. There is evidence that growing salinity variations may impact regional changes in river discharge along the Mediterranean coastlines, leading to a substantial land shift in the basin’s eastern regions. Even though Mediterranean circulation patterns can be altered, global sea-level rise will dominate future Mediterranean Sea-level change [59][26]. This pattern might result in local height fluctuations of up to 10 cm. Along the Mediterranean coast, increased CO2 absorption by the seas and acidification of 0.15 to 0.41 pH units [60][27] are anticipated to induce significant impacts.
Aside from these changes, the consequences of CC on people could affect infrastructure and ecosystems. Between 1960 and 2015, the population of Middle Eastern and North African (MENA) countries doubled, while urbanization increased from 35% to 64%. [18][28]. Due to the possibility of substantial yield gains in many southern and eastern land systems, agricultural land management is increasing, primarily via more excellent irrigation, with ramifications for water resources, biodiversity, and landscape functioning. Despite local advancements in wastewater treatment, air and water pollution continue to grow due to urbanization, traffic, and other factors. Political conflicts have a substantial environmental effect, and migratory pressure continues to affect economies with limited resources, making it more difficult for them to adapt to environmental changes [61][29].
Environmental, human health, human security, and food security are interconnected aspects of CC. The combination has foreseen the possibility of posing a threat and has taken precautions accordingly. Given the lack of resources, the exposure to all possible dangers is unlikely to be comparable to their overall exposure to any of them individually. The combination, on the other hand, may amplify the intensity impact that induces more frequent and consecutive episodes of stress, thereby worsening the countries’ situation. The five interconnected five domains are discussed in the following sub-topics.

3.1. Water Resources

In the basin’s southern and eastern regions, the nations of the Mediterranean experience severe water shortages. Mediterranean countries have to deal with the difficulty of satisfying rising water needs while having a limited freshwater supply. For every two Celsius of warming and the length of dry spells and droughts, fresh water is expected to go down by 2–15% [33][24]. Generally, the rivers will flow less, especially in the south and east, where water is in very short supply [62][30]. Most likely, the water in lakes and reservoirs will go down. Stream flow patterns are likely to change, with high spring flows from melting snow ending earlier, summer low flows getting more robust, and winter flows getting more significant and unpredictable [63][31]. In the future, the amount of water per person in the Mediterranean, which is already very low, will drop to less than 500 m3 per year. To make sure that aquatic ecosystems work well, it is crucial to meet environmental flow requirements. This outcome means that specific amounts of water will have to be kept in these systems, making them even harder for people to use [64][32].
Regularly, the coastal parts of the Mediterranean are impacted by flash floods induced by brief, intense rainfall in small catchments [36][33]. Extreme rainfall events will increase the likelihood of flooding, exacerbated by CC and non-climatic variables such as increased urbanization and inadequate stormwater management systems. Flooding is expected to become more common in many sections of the Mediterranean Basin due to inadequately designed stormwater management systems, impermeable urban surfaces, and people living in flood-prone places [36][33].

3.2. Managed Ecosystems

The Mediterranean Basin’s forest, wetland, coastal, and marine ecosystems are affected by seasonal fluctuation in the mean temperature and precipitation [56][21]. The diversity and long-term viability of Mediterranean land ecosystems may be most jeopardized by increased aridity brought on by decreased precipitation and rising temperatures [65][34]. Greater fire danger, longer fire seasons, and more catastrophic wildfires are predicted due to changing climate, increased heat waves, dryness, and land use [18][28]. Water levels are also decreasing, and the water quality is deteriorating, significantly impacting freshwater ecosystems [66][35]. Urbanization, agricultural abandonment, biological invasions, pollution, and overexploitation impact the structure and function of species, populations, communities and terrestrial ecosystems in the area [67][36]. As a result, the benefits and services of the Mediterranean may be at risk. The changes can be explored in many fields including renewable natural resources (such as food, medicine, and wood), environmental services (such as conservation of biodiversity, soils, and water, regulation of air quality and climate, and carbon storage), and social services (such as recreational, educational, and leisure opportunities, and traditional cultural values) [68][37].

3.3. Food Production and Security

Agriculture and fisheries are changing Mediterranean food production in social, economic, and ecological ways [69][38]. As the world’s population grows and diets change, so will the need for food, agricultural products, fish, and animal products. Crop illnesses, yield reductions, and more significant production variability may all occur due to extreme weather events like heat waves, cold snaps, or heavy rainfall during critical phenological stages. Many winter and spring crops, particularly in the southern Mediterranean, are expected to be affected by CC [70][39].
Olive production will be harmed due to rising irrigation demands due to CC [71][40]. Local and regional discrepancies will arise, while the influence on aggregate production is not anticipated to be significant [72][41]. It is anticipated that the phenological cycle of grapevines would shift toward shorter length and earlier blooming, accompanied by increased vulnerability to severe events and water stress [73][42]. These circumstances may also affect the quality of grapes. Flowering and chilling accumulation are also anticipated to influence fruit tree output [74][43]. Reduced water, such as in tomatoes, will be the primary factor restricting crop yields [75][44]. However, water-saving measures might be devised to enhance crops’ quality and nutritional value while maintaining appropriate output levels [76][45]. Due to CO2-fertilization effects, yield improvements may occur in some crops, which might boost water usage efficiency and biomass output, even though the intricate interactions among the numerous components and the present knowledge gaps suggest significant uncertainty [77][46]. In addition, these yields are anticipated to decline in quality (e.g., a fall in the protein content of cereals) [78][47]. In some regions, sea-level rise and ground subsidence may severely diminish agricultural land. The consequences of sea-level rise will impose more restrictions on agricultural land, notably in the Nile Delta and other productive delta regions [79][48].

3.4. Human Health

Heat, cold, drought, and storms (direct factors) as well as food quality, food availability, pollution, and the affect CC has on social and cultural issues, and the subsequent impact on human health, are all substantial. The degree and timing of the relevant effects vary according to the local environmental circumstances and the population’s susceptibility [18][28]. Along the Mediterranean Basin’s coastlines and in heavily populated metropolitan areas, there are locations with particularly considerable variations in ambient temperature and significant heatwaves [80][49].
High ambient temperatures (often coupled with relative humidity) exceed the land’s inherent ability to disperse heat. As a result, heat-related illnesses and deaths are a possibility, with the elderly, youngsters, and people with preexisting or present medical issues being more susceptible [81][50]. A rise in heatwave severity and frequency, or a shift in seasonality, presents substantial health hazards for vulnerable people, including the poor, those living in inadequate housing, and those with limited access to air conditioning [82][51].
Temperature-related disease and mortality rates will rise in the Mediterranean region in the coming decades if people do not prepare themselves for CC and public education, while healthcare systems are not up to pace [83][52]. The health of the elderly in all Mediterranean countries will become more problematic during heat waves as the population’s life expectancy increases. Climate change may affect the spread of vector-borne diseases due to its effects on the life cycles of vector species, pathogenic organisms, and reservoir organisms [84][53].

3.5. Human Security

As a result of natural disasters, societal unrest, or a combination of the two, people’s safety is at risk [85][54]. There was an 87% rise in the world’s population between 1970 and 2010; however, the populations in flood plains and cyclone-prone beaches grew by 114% and 198% [86][55]. More than a third of the inhabitants in the Mediterranean Basin live within walking distance of the sea. As a result of the small tidal range and relatively infrequent storm surges, coastal infrastructure, land use patterns, and human settlements have developed close to mean sea level [87][56]. Sea-level rise is expected to impact Mediterranean coastal dangers [88][57] significantly. Wave overtopping is a significant problem in Northern and Southern Mediterranean ports [87][56]. Morocco, Algeria, Libya, Egypt, Palestine, and Syria are among these countries [89][58]. With rising sea levels and local ground subsidence, port cities with a population in excess of one million may be at greater risk of catastrophic storm surge flooding [90][59]. By 2050, half of the 20 cities with the most significant yearly increase in damages will be in the Mediterranean, according to lower sea-level rise scenarios and current adaptation efforts [91][60]. More than 11% of North African countries’ populations would be displaced if sea levels rose by one meter.
As sea levels rise, saltwater intrusion will become more prevalent in coastal areas. Saline intrusion negatively influences around 30% of Egypt’s irrigated crops [92][61]. Salt-affected soils are found in 60% of the Northern agricultural area and 20% of the Middle and Southern Delta areas. In order to accommodate Egypt’s rising population, the environment is deteriorating [93][62]. In addition, there is a risk that environmental stressors, such as drought, would exacerbate social unrest and lead to a mass exodus. Then resources would be few, and attempts to reduce one risk may harm human community resilience or worsen other threats. The Mediterranean Basin has traditionally been unstable due to its cultural, geographic, and economic complexity [90][59].
Human security in the Mediterranean Basin is in danger due to the increased stress from CC, making the region’s residents more vulnerable and raising their level of anxiety [94][63]. The vulnerability has also been exacerbated by environmental mismanagement and overexploitation. The primary causes are the depletion of natural resources on land and at sea, desertification in the northern hemisphere, and the resulting food shortages (particularly in the Middle East and North Africa) [18][28].

References

  1. Picotti, V.; Negri, A.; Capaccioni, B. The geological origins and paleoceanographic history of the Mediterranean Region: Tethys to present. In The Mediterranean Sea; Springer: Dordrecht, The Netherlands, 2014; pp. 3–10.
  2. Koelsch, W.A. Ellen Semple’s Geography of the Mediterranean Region: The Biography of a Book; Northeastern Geographer: Guwahati, India, 2019; Volume 11.
  3. Doak, B.R. The Oxford Handbook of the Phoenician and Punic Mediterranean. In Oxford Handbooks; Oxford University Press: Oxford, UK, 2019.
  4. Kundzewicz, Z.W.; Pińskwar, I.; Koutsoyiannis, D. Variability of global mean annual temperature is significantly influenced by the rhythm of ocean-atmosphere oscillations. Sci. Total Environ. 2020, 747, 141256.
  5. Underwood, E.C.; Viers, J.H.; Klausmeyer, K.R.; Cox, R.L.; Shaw, M.R. Mediterranean climatic regions (MCRs). Divers. Distrib. 2009, 15, 188–197.
  6. Del Pozo, A.; Brunel-Saldias, N.; Engler, A.; Ortega-Farias, S.; Acevedo-Opazo, C.; Lobos, G.A.; Jara-Rojas, R.; Molina-Montenegro, M.A. Climate change impacts and adaptation strategies of agriculture in Mediterranean-climate regions (MCRs). Sustainability 2019, 11, 2769.
  7. Polade, S.D.; Gershunov, A.; Cayan, D.R.; Dettinger, M.D.; Pierce, D.W. Precipitation in a warming world: Assessing projected hydro-climate changes in California and other Mediterranean climate regions. Sci. Rep. 2017, 7, 10783.
  8. Raza, A.; Razzaq, A.; Mehmood, S.S.; Zou, X.; Zhang, X.; Lv, Y.; Xu, J. Impact of climate change on crops adaptation and strategies to tackle its outcome: A review. Plants 2019, 8, 34.
  9. Bangelesa, F.F. Impacts of Climate Variability and Change on Maize Zea mays Production in Tropical Africa. Ph.D. Thesis, Universität Würzburg, Wuerzburg, Germany, 2022.
  10. Garreaud, R.D.; Alvarez-Garreton, C.; Barichivich, J.; Boisier, J.P.; Christie, D.; Galleguillos, M.; LeQuesne, C.; McPhee, J.; Zambrano-Bigiarini, M. The 2010–2015 megadrought in central Chile: Impacts on regional hydroclimate and vegetation. Hydrol. Earth Syst. Sci. 2017, 21, 6307–6327.
  11. Lawrence, J.E.; Lunde, K.B.; Mazor, R.D.; Bêche, L.A.; McElravy, E.P.; Resh, V.H. Long-term macroinvertebrate responses to climate change: Implications for biological assessment in mediterranean-climate streams. J. N. Am. Benthol. Soc. 2010, 29, 1424–1440.
  12. Daryanto, S.; Wang, L.; Jacinthe, P.A. Global synthesis of drought effects on cereal, legume, tuber and root crops production: A review. Agric. Water Manag. 2017, 179, 18–33.
  13. Del Pozo, A.; Yáñez, A.; Matus, I.A.; Tapia, G.; Castillo, D.; Sanchez-Jardón, L.; Araus, J.L. Physiological traits associated with wheat yield potential and performance under water-stress in a Mediterranean environment. Front. Plant Sci. 2016, 7, 987.
  14. Shao, R.; Jia, S.; Tang, Y.; Zhang, J.; Li, H.; Li, L.; Chen, J.; Guo, J.; Wang, H.; Yang, Q.; et al. Soil water deficit suppresses development of maize ear by altering metabolism and photosynthesis. Environ. Exp. Bot. 2021, 192, 104651.
  15. Farooq, M.; Gogoi, N.; Barthakur, S.; Baroowa, B.; Bharadwaj, N.; Alghamdi, S.S.; Siddique, K.H. Drought stress in grain legumes during reproduction and grain filling. J. Agron. Crop Sci. 2017, 203, 81–102.
  16. Zhao, W.; Liu, L.; Shen, Q.; Yang, J.; Han, X.; Tian, F.; Wu, J. Effects of water stress on photosynthesis, yield, and water use efficiency in winter wheat. Water 2020, 12, 2127.
  17. Yáñez, A.; Tapia, G.; Guerra, F.; Del Pozo, A. Stem carbohydrate dynamics and expression of genes involved in fructan accumulation and remobilization during grain growth in wheat (Triticum aestivum L.) genotypes with contrasting tolerance to water stress. PLoS ONE 2017, 12, e0177667.
  18. Tanasijevic, L.; Todorovic, M.; Pereira, L.S.; Pizzigalli, C.; Lionello, P. Impacts of climate change on olive crop evapotranspiration and irrigation requirements in the Mediterranean region. Agric. Water Manag. 2014, 144, 54–68.
  19. Oury, V.; Tardieu, F.; Turc, O. Ovary apical abortion under water deficit is caused by changes in sequential development of ovaries and in silk growth rate in maize. Plant Physiol. 2016, 171, 986–996.
  20. Corell, M.; Pérez-López, D.; Andreu, L.; Recena, R.; Centeno, A.; Galindo, A.; Moriana, A.; Martín-Palomo, M. Yield response of a mature hedgerow oil olive orchard to different levels of water stress during pit hardening. Agric. Water Manag. 2022, 261, 107374.
  21. Guiot, J.; Cramer, W. Climate change: The 2015 Paris Agreement thresholds and Mediterranean basin ecosystems. Science 2016, 354, 465–468.
  22. Shindell, D.; Ru, M.; Zhang, Y.; Seltzer, K.; Faluvegi, G.; Nazarenko, L.; Schmidt, G.A.; Parsons, L.; Challapalli, A.; Yang, L.; et al. Temporal and spatial distribution of health, labor, and crop benefits of climate change mitigation in the United States. Proc. Natl. Acad. Sci. USA 2021, 118, e2104061118.
  23. Marklein, A.; Elias, E.; Nico, P.; Steenwerth, K. Projected temperature increases may require shifts in the growing season of cool-season crops and the growing locations of warm-season crops. Sci. Total Environ. 2020, 746, 140918.
  24. Schleussner, C.F.; Lissner, T.K.; Fischer, E.M.; Wohland, J.; Perrette, M.; Golly, A.; Rogelj, J.; Childers, K.; Schewe, J.; Schaeffer, M.; et al. Differential climate impacts for policy-relevant limits to global warming: The case of 1.5 °C and 2 °C. Earth Syst. Dyn. 2016, 7, 327–351.
  25. Kelley, C.P.; Mohtadi, S.; Cane, M.A.; Seager, R.; Kushnir, Y. Climate change in the Fertile Crescent and implications of the recent Syrian drought. Proc. Natl. Acad. Sci. USA 2015, 112, 3241–3246.
  26. Adloff, F.; Somot, S.; Sevault, F.; Jorda, G.; Aznar, R.; Déqué, M.; Herrmann, M.; Marcos, M.; Dubois, C.; Padorno, E.; et al. Mediterranean Sea response to climate change in an ensemble of twenty first century scenarios. Clim. Dyn. 2015, 45, 2775–2802.
  27. Magnan, A.; Colombier, M.; Billé, R.; Joos, F.; Hoegh-Guldberg, O.; Pörtner, H.-O.; Waisman, H.; Spencer, T.; Gattuso, J.-P. Implications of the Paris agreement for the ocean. Nat. Clim. Change 2016, 6, 732–735.
  28. Wanyama, D.; Mighty, M.; Sim, S.; Koti, F. A spatial assessment of land suitability for maize farming in Kenya. Geocarto Int. 2021, 36, 1378–1395.
  29. Mueller, N.D.; Gerber, J.S.; Johnston, M.; Ray, D.K.; Ramankutty, N.; Foley, J.A. Closing yield gaps through nutrient and water management. Nature 2012, 490, 254–257.
  30. Greve, P.; Kahil, T.; Mochizuki, J.; Schinko, T.; Satoh, Y.; Burek, P.; Fischer, G.; Tramberend, S.; Burtscher, R.; Langan, S.; et al. Global assessment of water challenges under uncertainty in water scarcity projections. Nat. Sustain. 2018, 1, 486–494.
  31. Rottler, E.; Francke, T.; Bürger, G.; Bronstert, A. Long-term changes in central European river discharge for 1869–2016: Impact of changing snow covers, reservoir constructions and an intensified hydrological cycle. Hydrol. Earth Syst. Sci. 2020, 24, 1721–1740.
  32. Stein, E.D.; Gee, E.M.; Adams, J.B.; Irving, K.; Niekerk, L.V. Advancing the science of environmental flow management for protection of temporarily closed estuaries and coastal lagoons. Water 2021, 13, 595.
  33. Gaume, E.; Borga, M.; Llassat, M.C.; Maouche, S.; Lang, M.; Diakakis, M. Mediterranean extreme floods and flash floods. In A Scientific Update; IRD Editions: Paris, France, 2016; pp. 133–144.
  34. Gouveia, C.M.; Trigo, R.M.; Beguería, S.; Vicente-Serrano, S.M. Drought impacts on vegetation activity in the Mediterranean region: An assessment using remote sensing data and multi-scale drought indicators. Glob. Planet. Change 2017, 151, 15–27.
  35. Mishra, A.; Alnahit, A.; Campbell, B. Impact of land uses, drought, flood, wildfire, and cascading events on water quality and microbial communities: A review and analysis. J. Hydrol. 2021, 596, 125707.
  36. Penuelas, J.; Sardans, J.; Filella, I.; Estiarte, M.; Llusià, J.; Ogaya, R.; Carnicer, J.; Bartrons, M.; Rivas-Ubach, A.; Grau, O.; et al. Impacts of global change on Mediterranean forests and their services. Forests 2017, 8, 463.
  37. Liquete, C.; Piroddi, C.; Macías, D.; Druon, J.N.; Zulian, G. Ecosystem services sustainability in the Mediterranean Sea: Assessment of status and trends using multiple modelling approaches. Sci. Rep. 2016, 6, 34162.
  38. Paciello, M.C. Building Sustainable Agriculture for Food Security in the Euro-Mediterranean Area; Edizioni Nuova Cultura: Rome, Italy, 2015.
  39. Deryng, D.; Elliott, J.; Folberth, C.; Müller, C.; Pugh, T.A.M.; Boote, K.J.; Conway, D.; Ruane, A.C.; Gerten, D.; Jones, J.W.; et al. Regional disparities in the beneficial effects of rising CO2 concentrations on crop water productivity. Nat. Clim. Change 2016, 6, 786–790.
  40. Fraga, H.; Moriondo, M.; Leolini, L.; Santos, J.A. Mediterranean olive orchards under climate change: A review of future impacts and adaptation strategies. Agronomy 2020, 11, 56.
  41. Dechezleprêtre, A.; Sato, M. The impacts of environmental regulations on competitiveness. Rev. Environ. Econ. Policy 2017, 11, 183–205.
  42. Fraga, H.; García de Cortázar Atauri, I.; Malheiro, A.C.; Santos, J.A. Modelling climate change impacts on viticultural yield, phenology and stress conditions in Europe. Glob. Change Biol. 2016, 22, 3774–3788.
  43. Funes, I.; Aranda, X.; Biel, C.; Carbó, J.; Camps, F.; Molina, A.J.; De Herralde, F.; Grau, B.; Savé, R. Future climate change impacts on apple flowering date in a Mediterranean subbasin. Agric. Water Manag. 2016, 164, 19–27.
  44. Arbex de Castro Vilas Boas, A.; Page, D.; Giovinazzo, R.; Bertin, N.; Fanciullino, A.L. Combined effects of irrigation regime, genotype, and harvest stage determine tomato fruit quality and aptitude for processing into puree. Front. Plant Sci. 2017, 8, 1725.
  45. Tamburini, G.; Bommarco, R.; Wanger, T.C.; Kremen, C.; van der Heijden, M.G.; Liebman, M.; Hallin, S. Agricultural diversification promotes multiple ecosystem services without compromising yield. Sci. Adv. 2020, 6, eaba1715.
  46. Fitzgerald, G.J.; Tausz, M.; O’Leary, G.; Mollah, M.R.; Tausz-Posch, S.; Seneweera, S.; Mock, I.; Löw, M.; Partington, D.L.; McNeil, D.; et al. Elevated atmospheric can dramatically increase wheat yields in semi-arid environments and buffer against heat waves. Glob. Change Biol. 2016, 22, 2269–2284.
  47. Fernando, N.; Panozzo, J.; Tausz, M.; Norton, R.; Fitzgerald, G.; Khan, A.; Seneweera, S. Rising CO2 concentration altered wheat grain proteome and flour rheological characteristics. Food Chem. 2015, 170, 448–454.
  48. Rateb, A.; Abotalib, A.Z. Inferencing the land subsidence in the Nile Delta using Sentinel-1 satellites and GPS between 2015 and 2019. Sci. Total Environ. 2020, 729, 138868.
  49. Linares, C.; Martinez, G.S.; Kendrovski, V.; Diaz, J. A new integrative perspective on early warning systems for health in the context of climate change. Environ. Res. 2020, 187, 109623.
  50. Ebi, K.L.; Capon, A.; Berry, P.; Broderick, C.; de Dear, R.; Havenith, G.; Honda, Y.; Kovats, R.S.; Ma, W.; Malik, A.; et al. Hot weather and heat extremes: Health risks. Lancet 2021, 398, 698–708.
  51. Paz, S.; Negev, M.; Clermont, A.; Green, M.S. Health aspects of climate change in cities with Mediterranean climate, and local adaptation plans. Int. J. Environ. Res. Public Health 2016, 13, 438.
  52. Kreitlow, A.; Steffens, S.; Jablonka, A.; Kuhlmann, E. Support for global health and pandemic preparedness in medical education in Germany: Students as change agents. Int. J. Health Plan. Manag. 2021, 36, 112–123.
  53. Parham, P.E.; Waldock, J.; Christophides, G.K.; Hemming, D.; Agusto, F.; Evans, K.J.; Fefferman, N.; Gaff, H.; Gumel, A.; Michael, E.; et al. Climate, environmental and socio-economic change: Weighing up the balance in vector-borne disease transmission. Philos. Trans. R. Soc. B Biol. Sci. 2015, 370, 20130551.
  54. Field, C.B.; Barros, V.R. (Eds.) Climate Change 2014—Impacts, Adaptation and Vulnerability: Regional Aspects; Cambridge University Press: Cambridge, UK, 2014.
  55. Hallegatte, S. An Exploration of the Link between Development, Economic Growth, and Natural Risk; World Bank: Washington, DC, USA, 2014.
  56. Ranasinghe, R. On the need for a new generation of coastal change models for the 21st century. Sci. Rep. 2020, 10, 2010.
  57. Lionello, P.; Conte, D.; Marzo, L.; Scarascia, L. The contrasting effect of increasing mean sea level and decreasing storminess on the maximum water level during storms along the coast of the Mediterranean Sea in the mid 21st century. Glob. Planet. Change 2017, 151, 80–91.
  58. Satta, A.; Puddu, M.; Venturini, S.; Giupponi, C. Assessment of coastal risks to climate change related impacts at the regional scale: The case of the Mediterranean region. Int. J. Disaster Risk Reduct. 2017, 24, 284–296.
  59. Esteban, M.; Takagi, H.; Jamero, L.; Chadwick, C.; Avelino, J.E.; Mikami, T.; Fatma, D.; Yamamoto, L.; Thao, N.D.; Onuki, M.; et al. Adaptation to sea level rise: Learning from present examples of land subsidence. Ocean Coast. Manag. 2020, 189, 104852.
  60. Galeotti, M. The Economic Impacts of Climate Change in the Mediterranean. In Mediterranean Yearbook; IEMed: Barcelona, Spain, 2020.
  61. Al-Mannai, A.A. Assessment of Inundation Risk from Sea Level Rise and Critical Area for Barrier Construction: A GIS-Based Framework and Application on the Eastern Coastal Areas of Qatar. Ph.D. Thesis, University of East Anglia, Norwich, UK, 2021.
  62. Hammam, A.A.; Mohamed, E.S. Mapping soil salinity in the East Nile Delta using several methodological approaches of salinity assessment. Egypt. J. Remote Sens. Space Sci. 2020, 23, 125–131.
  63. Gleick, P.H. Water, drought, climate change, and conflict in Syria. Weather Clim. Soc. 2014, 6, 331–340.
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