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Desertification Indicator System for Mediterranean Europe


1. Definition

Name (ARTIFICIAL) HYDROLOGICAL REGULATION
Brief definition Proportion of the natural surface water resources of a basin which are artificially regulated.
Unit of measure %
Spatial scale  
Temporal scale Annual measures

2. Position within the logical framework DPSIR

Type of Indicator Pressure and response

3. Target and political pertinence

Objective

To indicate the stress on water resources usage and being a measure of how the socio-economic system hosted by the basin is dependent on the water resources. To provide a very significant synthetic figure of vulnerability to desertification in social and productive-economic systems.

Importance with respect to desertification The pressure of the scarcity of water leads to artificial works such as dams and channel structures to increase the proportion of the natural water resources that are regulated in time to guarantee a regular wate supply to satisfy the demand in the most unfavourable situations. In humid areas the percentage of natural water resources which are artificially regulated is frequently zero, because the minimum base flow of the river is higher than the required flow for consumption and there is no need to build any reservoir or structure except for the intake to the distribution network. Consequently, the greater the amount of regulated resources compared to the total amount, the higher degree of water resource usage and the greater the potential for stress on water use. Very high degree of hydrological regulation characterises many of the areas in the world where desertification is an active, current phenomena.
International Conventions and agreements  
Secondary objectives of the indicator The presence of very high (>80%) values of the indicator might be considered as a warning of sustainability of the social and economic system because of water resources scarcity in case of severe drought.

4. Methodological description and basic definitions

Definitions and basic concepts

A river with no artificial regulation has a certain base flow determined by climate and morphology, land cover and geology of the basin. This base flow is, in general, very low in the Mediterranean rivers. One of the consequences of the existence of a dam is the increase of the base flow with regard to the total discharge of the river (see the Fig. 1) and so it is an indicator of the need of regulation because of water scarcity.

Fig. 1: Rating curves comparison, Piedra River

The comparison of the base flows of both the natural regulation situation and the real regulation (man-made) will determine the existence of dams and other regulation structures as well as the degree of the regulation.

Benchmarks Indication of the values/ranges of value
  • 50% represent a very high degree of artificial regulation, but
  • percentages over 80 are present in some Mediterranean basins indicating extreme stress associated with water resources usage.
Methods of measurement

This indicator should be obtained from the water administration authorities. Nevertheless the rationale of calculation can be summarized with the aid of the above figure taken as an example from the Piedra river in Spain:

1. The black curve represent the natural situation. The horizontal light blue line represents the minimum naturally regulated discharge guaranteed at about 1.3 m3/s. The ratio between the surface under this light blue line and x axis divided betweem the surface under the dark blue line and the x axis represent the natural regulation of the river.

2. Because the naturally regulated discharge of 1.3 m3/s is not enough to satisfy the water demand a reservoir is built. The red curve corresponds to the typical discharge after reservoir construction. The area between the red curve and the X-axis represent the total natural resources and is coincident with the area between the black line and the X-axis (total natural resources are the same with or without reservoir).

3. The graph shows the annual hydrographs of the Piedra River in Spain, in the natural situation (black) and the artificially regulated situation (red). The regulated situation corresponds to the outlet of a reservoir built and the natural situation is the same outlet before the reservoir construction. Once the reservoir is constructed the Piedra river basin upwaters is artificially regulated. The real rating curve (red) is adapted to the demand providing high discharges in summertime (irrigation), so we have 100% of artificial hydrological regulation.

4. In practice the question is more complex as we are dealing with a basin with several demands in several points and several tributaries of a main river, with different natural resources, proportions of water uses, which return to the rivers as waste water (which may be used downstream after purification) or for other uses less dependent in water quality.

The scheme of the Fig. 2 depicts a complex real situation as described. The % of artificial regulation will be determined considering the global system of demands, reservoirs and wastewater releases and reuses.

Fig. 2 Complex combination of water supply and use to be found in most large river basins

5. From a strict point of view the indicator defined here should be the difference between the percentage of regulation which characterises the natural situation and the percentage of regulation in the second situation, meaning thus the increase in regulation obtained. In practice as Mediterranean and semi-arid lands rivers very frequently present a near zero degree of natural regulation, the natural regulation is neglected and then we speak of regulation in absolute terms.

Limits of the indicator The natural discharge of the river in its natural status conditions is the starting point of the indicator and every river presents its own unique features. In this sense the indicator maybe relative, but in the Mediterranean areas this effect is not relevant, as the differences among river regime types in different basins, are not significant for the purposes of the indicator. The indicator is applicable to basins of large size, tens of thousands of square kilometres.
Linkages with other indicators Water scarcity; Rainfall; External water resources

5. Evaluation of data needs and availability

Data required to calculate the indicator Complete scheme of the basin water resource use and natural resources should be calculated by water administration of the basin. Annual rating curves (of discharge) in a certain point of the river's watercourse for both situations: the natural and the real regulation are also needed.
Data sources The data needed could be provided by the River Basin Authorities, and also the National Hydrological Plan in its different applications for the various Spanish basins.
Availability of data from national and international sources River Basin Authorities.

6. Institutions that have participated in developing the indicator

Main institutions responsible Dirección General para la Biodiversidad. Ministerio de Medio Ambiente. Spain.

Other contributing organizations  

7. Additional information

Bibliography Hidrología Subterránea. Emilio Custodio (ed.) Ediciones Omega. Barcelona. 1976. (pp.399-405)
Other references Plan Hidrológico Nacional. España. Ministerio de Medio Ambiente. Hydrological Plans for the main Spanish Basins
Contacts Name and address

Leopoldo Rojo Serrano
Dirección General para la Biodiversidad
Ministerio de Medio Ambiente
Gran Vía de San Francisco
428005 Madrid (Spain)

<lrojo@mma.es>