Utilization and conservation of groundwater
In the middle-latitude zone, the natural vegetation changes from
forests to grasslands near an isohyet of 500 mm/year, and from grasslands to
deserts near that of 250 mm/year. The amount of recharge to the groundwater is
the difference between the annual precipitation and the annual evaporation,
provided that no surface run-off occurs. In the case of a dry climate with
precipitation less than 500 mm/year and where the potential evaporation far
exceeds the annual precipitation, as in drylands, the amount of groundwater
recharge is heavily dependent on the actual evaporation lost from the land
surface. Deforestation and desertification result in a decrease of local
precipitation due to positive feedback effects, as discussed above. On the other
hand, it is quite difficult, if not impossible, to increase the amount of local
precipitation anthropogenically.
For the sustainable use of drylands, it is desirable to develop
such methods that induce positive feedback effects to increase the amount of
available water. The amount of actual evaporation lost from the soil surface is
an issue of human intervention in drylands. Dry farming is a technique to
maximize the input from meteoric water into the soil, and at the same time to
minimize the evaporation loss from the soil surface. Deep cultivation of soil
before the rainy or snowy season is a technique to introduce rain or snow-melt
water into deep soil layers. The evaporation loss of soil moisture could be
decreased by forming a loose surface layer in which capillary continuity of soil
pores is discontinued by disturbing or crushing the surface soil.
Yamanaka et al. (1994) conducted an experiment that contributed to
the increased understanding of the dynamic behaviour of water vapour in the soil
layer and the role of a surface dry layer (SDL) on soil evaporation. When the
SDL is formed during the evaporation process at the bare soil surface, the water
vapour in the SDL plays an important role by connecting the liquid water in the
soil and the water vapour in the atmosphere. The thickness of the SDL is about
4-5 cm, and the lower boundary of the SDL coincides with a surface where soil
water vaporizes. The SDL acts as a strong barrier against the transport of the
water vapour in the soil evaporated from the evaporation surface below the SDL.
Since the experimental result mentioned above is obtained for the
diurnal change in water vapour concentration within a standard sand layer only,
its applicability is of limited nature. Future progress in research on the
dynamic behaviour of transport processes of heat and water near the soil
surface, including the dynamic behaviour on a much longer time-scale of seasons
and years, and for different soil types, may contribute to the proper management
of soil and groundwater in arid lands.
Groundwater, soil water, river water, lake water, and mountain
glaciers are linked through the regional hydrological cycle. However, in such
hydrological characteristics as the residence time, water storage, water
quality, and recharge and discharge processes, they are quite different from
each other. For the proper use of groundwater in arid lands, the conjunctive use
of waters with different hydrological characteristics is necessary. The science
of hydrology may contribute to an increased understanding of hydrological
processes and hydrological characteristics of natural waters, especially for
groundwater in arid
lands.