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Albania

Fresh water resources

Fresh water resources in numbers - Albania

The area surrounding Albania has relatively abundant fresh water resources. Seven main rivers run from east to west in Albania. The contribution of rivers discharge into the Adriatic sea is very large (95%), compared to the discharge into Ionian sea (5%). The total volume of water flow is 39,220 x 106 m3/year. There are two characteristic periods in the year, in terms of the water flow: the wet period, (October - May) and the dry one (June - September). 86% of the annual water flow is discharged during the wet period and 8% during the dry one. June is the transition period, accounting for 6% of the annual water flow (5).

The agricultural sector is the biggest consumer of fresh water (60% of the total water use) (22).

Vulnerabilities - Albania

A decrease in the long term mean annual and seasonal runoff is projected for the whole territory of Albania; according to model outputs a small decrease in the long term mean annual runoff is forecasted of 6.3% to 9.1% in 2025. A further decrease is expected towards 2100 (5).


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Fresh water resources in numbers - Mediterranean basin

The Mediterranean basin is 3,800 km long and 400 to 740 km wide. It takes 90 years for the water in this sea to be completely renewed. Hence, it is especially susceptibility to pollution. The population is between 150 and 250 million depending on whether just the actual coastal strip is taken into account or the drainage basin of the Mediterranean (4).

Vulnerabilities - Mediterranean

Water availability in the Mediterranean is highly sensitive to changes in climate conditions. In the last century the Mediterranean basin has experienced up to 20 % reduction in precipitation (2). Such a trend is expected to worsen with increasing demand for water and reduction in rainfall in the region (6,7). Future projection of this trend will reduce drastically water supplies in these areas, affecting considerably the population and economy of the Mediterranean countries (8).


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Fresh water resources in numbers - Europe

By 2005 for Europe as a whole (including New Member States and Accession Countries) some 38% of the abstracted water was used for agricultural purposes, while domestic uses, industry and energy production account for 18%, 11%, and 33%, respectively (2). However, large differences exist across the continent. In Malta, Cyprus and Turkey, for example, almost 80% of the abstracted water is used for agriculture, and in the southwestern countries (Portugal, Spain, France, Italy, Greece) still about 46% of the abstracted water is used for this purpose. In the central and northern countries (Austria, Belgium, Denmark, Germany, Ireland, Luxembourg, Netherlands, UK, and Scandinavia), to the contrary, agricultural use of the abstracted water is limited to less than 5%, while more than 50% of the abstracted water goes into energy production (a non-consumptive use) (2).

Southern countries use ca. three times more water per unit of irrigated land than other parts of Europe. The large amount of water dedicated to irrigation in the southern countries is problematic since most of these countries have been classified as water stressed, and face problems associated with groundwater over-abstraction such as aquifer depletion and salt water intrusion (3).

Fresh water resources in numbers - Wordwide

In the absence of climate change, the future population in water-stressed watersheds depends on population scenario and by 2025 ranges from 2.9 to 3.3 billion people (36–40% of the world’s population). By 2055 5.6 billion people would live in water-stressed watersheds under the A2 population future (the A2 storyline has the largest population), and ‘‘only’’ 3.4 billion under A1/B1(1).

Climate change increases water resources stresses in some parts of the world where runoff decreases, including around the Mediterranean, in parts of Europe, central and southern America, and southern Africa. In other water-stressed parts of the world, particularly in southern and eastern Asia, climate change increases runoff, but this may not be very beneficial in practice because the increases tend to come during the wet season and the extra water may not be available during the dry season (1).

Europe: five lake categories

There are almost one and a half million lakes in Europe, if small water bodies with an area down to 0.001 km2 are included. The total area of lakes is over 200,000 km2; in addition the manmade reservoirs cover almost 100,000 km2. The response of European lakes to climate change can be discussed by dividing the lakes into five categories (21):


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South-eastern Europe: four types of lakes

In order to discuss the effect of climate change to lakes in south-eastern Europe, the region is divided into three climatic sub regions. The main characteristic in this subdivision is the mean temperature in January, because the severity of winter has an essential influence to the lakes. The sub regions and the anticipated influences of climate change, around the year 2050, are as follows (21):


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Adaptation strategies - Mediterranean

In southern Europe, to compensate for increased climate related risks (lowering of the water table, salinisation, eutrophication, species loss), a lessening of the overall human burden on water resources is needed. This would involve stimulating water saving in agriculture, relocating intensive farming to less environmentally sensitive areas and reducing diffuse pollution, increasing the recycling of water, increasing the efficiency of water allocation among different users, favouring the recharge of aquifers and restoring riparian vegetation, among others (19).

Managed aquifer recharge

Comprehensive management approaches to water resources that integrate ground water and surface water may greatly reduce human vulnerability to climate extremes and change, and promote global water and food security. Conjunctive uses of ground water and surface water that use surface water for irrigation and water supply during wet periods, and ground water during drought (24), are likely to prove essential. Managed aquifer recharge wherein excess surface water, desalinated water and treated waste water are stored in depleted aquifers could also sup­plement groundwater storage for use during droughts (25,26). Indeed, the use of aquifers as natural storage reservoirs avoids many of the problems of evaporative losses and ecosystem impacts asso­ciated with large, constructed surface-water reservoirs.

Adaptation strategies - Albania

Across Albania there is a high density of small rural dams; 640 small- to medium-size reservoirs with a cumulative storage capacity of about 0.6 billion m3. Developed for irrigation from the 1960s–80s, there are important opportunities today to rationalize and modernize the dams, improve their use, and raise Albania’s capacity to manage increasing hydrological variability. Such measures could be further supported through rehabilitation of main irrigation canals and better incentives for the adoption of efficient irrigation systems(20).


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References

The references below are cited in full in a separate map 'References'. Please click here if you are looking for the full references for Albania.

  1. Arnell (2004)
  2. Eisenreich (2005)
  3. EEA (2003); EEA (WQ03b), both in: Eisenreich (2005)
  4. European Environment Agency (EEA) (2005)
  5. Republic of Albania, Ministry of Environment (2002)
  6. Arnell (2004)
  7. Rosato and Giupponi (2003), in: European Environment Agency (EEA) (2005)
  8. Trigo et al. (2004), in: Eisenreich (2005)
  9. Hulme (1999); UNEP/MAP/MED/POL (2003), both in: European Environment Agency (EEA) (2005)
  10. Alcamo et al. (2007)
  11. Santos et al. (2002), in: Alcamo et al. (2007)
  12. WHO (2007)
  13. Arnell (2003), in: Arnell (2004)
  14. Eitzinger et al.(2003), in: European Environment Agency (EEA) (2005)
  15. Mimikou et al.(2000), in: European Environment Agency (EEA) (2005)
  16. Williams (2001); Zalidis et al. (2002), both in: Alcamo et al. (2007)
  17. Döll (2002), in: European Environment Agency (EEA) (2005)
  18. Lehner et al. (2006), in: Alcamo et al. (2007)
  19. Alvarez Cobelas et al. (2005), in: Alcamo et al. (2007)
  20. Worldbank (2009)
  21. Kuusisto (2004)
  22. Diku (2011)
  23. Chenoweth et al. (2011)
  24. Faunt (2009), in: Taylor et al. (2012)
  25. Scanlon et al. (2012), in: Taylor et al. (2012)
  26. Sukhija (2008), in: Taylor et al. (2012)

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