Agricultural hydrology
Study of agricultural water management, especially irrigation and drainage
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Through Irrigation, Drainage and Rain
Water balance components
The water balance components can be grouped into components corresponding to zones in a vertical cross-section in the soil forming reservoirs with inflow, outflow and storage of water:
- the surface reservoir (S)
- the root zone or unsaturated (vadose zone) (R) with mainly vertical flows
- the aquifer (Q) with mainly horizontal flows
- a transition zone (T) in which vertical and horizontal flows are converted
The general water balance reads:
- inflow = outflow + change of storage
and it is applicable to each of the reservoirs or a combination thereof.
In the following balances it is assumed that the water table is inside the transition zone.
Surface water balance
The incoming water balance components into the surface reservoir (S) are:
- Rai – Vertically incoming water to the surface e.g.: precipitation (including snow), rainfall, sprinkler irrigation
- Isu – Horizontally incoming surface water. This can consist of natural inundation or surface irrigation
The outgoing water balance components from the surface reservoir (S) are:
- Eva – Evaporation from open water on the soil surface (see Penman equation)
- Osu – Surface runoff (natural) or surface drainage (artificial)
- Inf – Infiltration of water through the soil surface into the root zone
The surface water balance reads:
- Rai + Isu = Eva + Inf + Osu + Ws, where Ws is the change of water storage on top of the soil surface
Root zone water balance
The incoming water balance components into the root zone (R) are:
- Inf – Infiltration of water through the soil surface into the root zone
- Cap – Capillary rise of water from the transition zone
The outgoing water balance components from the surface reservoir (R) are:
- Era – Actual evaporation or evapotranspiration from the root zone
- Per – Percolation of water from the unsaturated root zone into the transition zone
The root zone water balance reads:
- Inf + Cap = Era + Per + Wr, where Wr is the change of water storage in the root zone
Transition zone water balance
The incoming water balance components into the transition zone (T) are:
- Per – Percolation of water from the unsaturated root zone into the transition zone
- Lca – Infiltration of water from river, canal or drainage systems into the transition zone, often referred to as deep seepage losses
- Ugw – Vertically upward seepage of water from the aquifer into the saturated transition zone
The outgoing water balance components from the transition zone (T) are:
- Cap – Capillary rise of water into the root zone
- Dtr – Artificial horizontal subsurface drainage, see also Drainage system (agriculture)
- Dgw – Vertically downward drainage of water from the saturated transition zone into the aquifer
The water balance of the transition zone reads:
- Per + Lca + Ugw = Cap + Dtr + Dgw + Wt, where Wt is the change of water storage in the transition zone noticeable as a change of the level of the water table.
Aquifer water balance
The incoming water balance components into the aquifer (Q) are:
- Dgw – Vertically downward drainage of water from the saturated transition zone into the aquifer
- Iaq – Horizontally incoming groundwater into the aquifer
The outgoing water balance components from the aquifer (Q) are:
- Ugw – Vertically upward seepage of water from the aquifer into the saturated transition zone
- Oaq – Horizontally outgoing groundwater from the aquifer
- Wel – Discharge from (tube)wells placed in the aquifer
The water balance of the aquifer reads:
- Dgw + Iaq = Ugw + Wel + Oaq + Wq
where Wq is the change of water storage in the aquifer noticeable as a change of the artesian pressure.
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Specific water balances
Combined balances
Water balances can be made for a combination of two bordering vertical soil zones discerned, whereby the components constituting the inflow and outflow from one zone to the other will disappear.
In long term water balances (month, season, year), the storage terms are often negligible small. Omitting these leads to steady state or equilibrium water balances.
Combination of surface reservoir (S)and root zone (R) in steady state yields the topsoil water balance :
- Rai + Isu + Cap = Eva + Era + Osu + Per, where the linkage factor Inf has disappeared.
Combination of root zone (R) and transition zone (T) in steady state yields the subsoil water balance :
- Inf + Lca + Ugw = Era + Dtr + Dgw, where Wr the linkage factors Per and Cap have disappeared.
Combination of transition zone (T) and aquifer (Q) in steady state yields the geohydrologic water balance :
- Per + Lca + Iaq = Cap + Dtr + Wel + Oaq, where Wr the linkage factors Ugw and Dgw have disappeared.
Combining the uppermost three water balances in steady state gives the agronomic water balance :
- Rai + Isu + Lca + Ugw = Eva + Era + Osu + Dtr + Dgw, where the linkage factors Inf, Per and Cap have disappeared.
Combining all four water balances in steady state gives the overall water balance :
- Rai + Isu + Lca + Iaq = Eva + Era + Osu + Dtr + Wel + Oaq, where the linkage factors Inf, Per, Cap, Ugw and Dgw have disappeared.
Water table outside transition zone
When the water table is above the soil surface, the balances containing the components Inf, Per, Cap are not appropriate as they do not exist. When the water table is inside the root zone, the balances containing the components Per, Cap are not appropriate as they do not exist. When the water table is below the transition zone, only the aquifer balance is appropriate.
Reduced number of zones
Under specific conditions it may be that no aquifer, transition zone or root zone is present. Water balances can be made omitting the absent zones.
Net and excess values
Vertical hydrological components along the boundary between two zones with arrows in the same direction can be combined into net values .
For example, : Npc = Per − Cap (net percolation), Ncp = Cap − Per (net capillary rise).
Horizontal hydrological components in the same zone with arrows in same direction can be combined into excess values .
For example, : Egio = Iaq − Oaq (excess groundwater inflow over outflow), Egoi = Oaq − Iaq (excess groundwater outflow over inflow).
Salt balances
Agricultural water balances are also used in the salt balances of irrigated lands.
Further, the salt and water balances are used in agro-hydro-salinity-drainage models like Saltmod.
Equally, they are used in groundwater salinity models like SahysMod which is a spatial variation of SaltMod using a polygonal network.
Irrigation and drainage requirements
The irrigation requirement (Irr) can be calculated from the topsoil water balance, the agronomic water balance or the overall water balance, as defined in the section "Combined balances", depending on the availability of data on the water balance components.
Considering surface irrigation, assuming the evaporation of surface water is negligibly small (Eva = 0), setting the actual evapotranspiration Era equal to the potential evapotranspiration (Epo) so that Era = Epo and setting the surface inflow Isu equal to Irr so that Isu = Irr, the balances give respectively:
- Irr = Epo + Osu + Per − Rai − Cap
- Irr = Epo + Osu + Dtr + Dgw − Rai − Lca − Ugw
- Irr = Epo + Osu + Dtr + Oaq − Rai − Lca − Iaq
Defining the irrigation efficiency as IEFF = Epo/Irr, i.e. the fraction of the irrigation water that is consumed by the crop, it is found respectively that :
- IEFF = 1 − (Osu + Per − Rai − Cap) / Irr
- IEFF = 1 − (Osu + Dtr + Dgw − Rai − Lca − Ugw) / Irr
- IEFF = 1 − (Osu + Dtr + Oaq − Rai − Lca − Iaq) / Irr
Likewise the safe yield of wells, extracting water from the aquifer without overexploitation, can be determined using the geohydrologic water balance or the overall water balance, as defined in the section "Combined balances", depending on the availability of data on the water balance components.
Similarly, the subsurface drainage requirement can be found from the drain discharge (Dtr) in the subsoil water balance, the agronomic water balance, the geohydrologic water balance or the overall water balance.
In the same fashion, the well drainage requirement can be found from well discharge (Wel) in the geohydrologic water balance or the overall water balance.
The subsurface drainage requirement and well drainage requirement play an important role in the design of agricultural drainage systems (references:, ).