To map the moisture distribution in the soil profile, the research employed geoelectrical techniques, validated by the gravimetric method (sample weighing). This methodology allowed for monitoring the soil's electrical resistivity, a parameter closely related to volumetric water content, up to a depth of 3 meters .
The study monitored three key phases, corresponding to the autumn-winter and pre-summer recharge periods.
November (initial phase): After the first autumn rains (58 mm), the grassed system already showed a higher water content, especially beyond 0.6 m depth. In contrast, the tilled system showed low and uniform water levels along the entire profile.
January (climate anomaly): Despite an additional 61 mm of rainfall, low precipitation combined with high temperatures caused water loss in the layers between 0.6 and 1.8 meters in the grassy system, due to transpiration of grass and olive trees. The tilled system, however, showed slight accumulation limited to the surface layers (0-0.9 m).
April (full recharge): Thanks to consistent rainfall (211 mm), both systems benefited from enrichment. However, the grassed system accumulated water in the deepest areas, essential for the olive tree roots, while the tilled system showed slow recharge, limited to the first 60 cm.
The superior water-absorbing properties of grassy soils lie in the soil's physical structure. Macroporosity is greater and more evenly distributed, thanks to the presence of "transmission pores" (50-500 μm) created by roots and earthworm activity.
Permeability: In grassed soil, water flows freely along the entire profile. In the tilled system, infiltration is impeded by the formation of surface crusts and a compact layer (tillage) that limits the vertical movement of the fluid.
Organic matter: the addition of plant residues and prunings improves water retention and acts as a natural mulch, drastically reducing direct evaporation from the soil.
Despite its greater storage capacity, the grassed system consumes more water. Between November and January, grassed consumption was almost double that of processed crops. This is due to the "double pump" of transpiration: that of the grasses and that of the olive trees, which in mild climates never completely shut down their metabolism.
In spring, consumption by the grassed system increased further (+32%), but the processed system also recorded a peak (+55%) due to the greater availability of surface water and the increase in environmental demand (ETo).
Geoelectric technology has confirmed that grassing, if well managed, is a powerful tool for conserving deep-seated water reserves , often overlooked but vital during summer droughts . However, to prevent water competition between grass and olive trees from becoming harmful, management must be strategic:
Timing of mowing: the grass cover must be removed before the critical stages of the olive tree (flowering and fruit set).
Mulching effect: the residues left on the surface protect the soil, although in areas at high fire risk a light surface burial may be necessary.
In short, grassing transforms the soil into a more efficient "sponge," capable of exploiting even light rainfall to replenish the olive grove's deep reserves.