As. Sheta et al., Nature and composition of newly formed precipitates in relationship to characteristics of groundwater in arid environment, ARID SOIL R, 14(4), 2000, pp. 387-401
Chemical characteristics of groundwater and the composition of newly formed
precipitates are critical in the management of modern irrigated agricultur
e in arid regions. Water samples representing the main aquifers in Riyadh r
egion, Saudi Arabia, and solid samples from the newly formed precipitates w
ere studied. Results showed that water temperature varied between 30.3-69 d
egrees C, being higher in the deep aquifer and low in the relatively shallo
w aquifers. Initial water pH ranged from 6.39-7.92, increasing to 7.65-8.20
at atmospheric conditions. Shallow aquifer waters were categorized into su
lfate-type and Cl- or no-dominant type waters, while the deep aquifers were
characterized as Cl- type and no-dominant type. Soluble soluble Fe and Mn
ranged from 3.15 to 18.82, 0.10 to 17.30, and 0.01 to H4SiO4, 0.32 mg L-1,
respectively. Calculation of saturation indices from water composition at i
nitial, closed and equilibrium conditions indicated that changes in pH and
water temperature cause major chemical changes in the water favoring the pr
ecipitation of carbonates and Fe-silicates. Data of total chemical analysis
indicated that carbonates are present in all samples and constituted up to
976 g kg(-1) of the precipitates formed from the deep aquifer water in the
irrigation tubes. Amorphous and/or crystalline Fe compounds were the domin
ant fractions in the surface crust precipitates, while crystalline Fe compo
unds was the dominant form in the precipitates in irrigation tubes and in t
he cooling reservoir. XRD data confirmed that aragonite was the dominant ca
rbonate mineral in the precipitates formed from the deep aquifer water. Cal
cite and Mg-calcite were detected in considerably low quantities. Poorly cr
ystalline Fe-oxide minerals were present in all the precipitate samples. Re
sults suggested that formation of precipitates either in cooling reservoirs
or in irrigation systems can be minimized by controlling the degassing thr
ough keeping the system closed, lowering the pH through the injection of in
organic acids in the system or both.