Regionalized Water Balances

Overview

Consistent water balances have been established for all six water regions in the study area.
A standardized system of documenting all base data that was used for quantifying the water supply and demand for the base year 2000. The data were submitted by all project partners as part of their water plan reports. The project team has then established a harmonized version of the water supply and demand data, using the (few) official data, supplementary data from other data sets, and using estimates to fill in missing data. All water balances from the water regions were linked together into an overall water balance.

Standard water quality categories

Water supply
Major springs are located in the southwest along the valley slopes. In the northern and center parts of the valley such productive springs are located also within the valley floor. Wells are often located in or near the bigger settlements (map).
“Locally renewable” water sources are virtually nonexistent because precipitation is very low. “Locally available” water sources (local springs and wells that are renewed outside the valley) make up 255 million cubic meters per year (MCM/yr) but are inadequately distributed. This water supply translates to an availability of about 1000 m²/cap.yr or 2000 m²/ha.yr, which is abundant. In addition to the “locally available” water, about 209 MCM/yr of water are “imported” into the valley from outside to make up a 464 MCM/yr of “total available” water.

Water usage
A spatial annual water balance was made on the level of six water regions. It was not possible to model a detailed sub-regional water balance because information about water supply and distribution (e.g. discharge of all wells and springs, transfer points for "imports" of surface water or wastewater, complete water channel network) was insufficient.
Domestic water use accounts for only about 5 % of the total water demand. Even with an increase of the per-capita usage to luxury standards for the population in Jordan and Palestine the domestic demand can be easily met in all regions through available local drinking water quality sources.
The regional risk of water shortage is much higher in the regions east of the river Jordan than in the west. The east has much less “locally available” water and is much more dependent on imported water. The self- sufficiency of "locally available" water supply for local demand is particularly high in the Tubas (100 %) and the Bet Shean (84 %) regions, and low in the Shayk Husayn and Mashare regions (14 % and 20 %). The necessary "imports" of water from outside the target area to match the usage is a major risk for water shortage, particularly if these come from regions that compete for water.
Furthermore, local water in the east has a far lower quality than in the west. The southeastern region (Karama) has no drinking water available to serve the population, while in the other regions most drinking water is used for agriculture.
About 95 % of the current usage is from agricultural activities, mainly irrigation  (e.g.irrigation of fruit orchards & field crops, or fishponds). In the overall Lower Jordan Valley there is is about 6 times more drinking water quality available than presently used for domestic purposes.

Example results

Results show that very little of the available water is indeed being used for the population while most drinking water is used for agriculture.

System overviews:

Data tables:

Maps:

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