Changes in hydraulic conductivity of soils varying in calcite content under cycles of irrigation with saline-sodic and simulated rain water

Abstract Soil infiltration problems occur as a result of alternating irrigation with saline-sodic waters and monsoon rainfall. Hydraulic conductivity (K) and related soil properties of a non-calcareous (CaCO3 0.8%) and a calcareous soil (25.7%) having similar textural constituents were monitored. The soils were subjected to six consecutive cycles of irrigation with saline waters (SW) of sodium adsorption ratio (SAR), 10, 20 or 30 (mmol/l)1/2, but of similar electrolyte concentration (EC; 80 mEq/l), and each followed by simulated rain water (SRW) (electrical conductivity <0.02 dS/m). Results are presented in terms of relative K i.e. Kr=Ksw/Ktw where Ktw is steady state K measured separately under application with tap water (ECw 0.54 dS/m, SAR 0.9). For irrigation with SW alone, Kr values were reduced to 0.95, 0.79 and 0.70 at SAR of 10, 20 and 30, respectively, in non-calcareous soil. The corresponding values of 0.95, 0.87 and 0.79 were slightly higher in calcareous soil. Severe reductions in Kr were observed in both the soils when subjected to alternate use of SW and SRW (Kr=0.22, 0.03 and 0.02 in non-calcareous, and 0.57, 0.17 and 0.07 in calcareous soil). About half of the reductions in Kr were reversible when SW was subsequently applied. Depth distributions of salinity, pH, dispersible clay and hydraulic head indicate that disaggregation and dispersion of surface soil was the cause of reduced K with SRW, whereas “washed in” sub-soil became restrictive and controlled the K values with SW under alternations of SW and SRW. Salt release (<1 mEq/l) was insufficient to avoid dispersion and sustain K even in the calcareous soil. For evaluating the infiltration hazard of saline-sodic water, measurements of stabilized K values after consecutive cycles of SW and SRW should serve as a better diagnostic criteria under monsoonal climates than threshold EC–SAR combinations.

[1]  I. Shainberg,et al.  Salt Effects on the Hydraulic Conductivity of a Sandy Soil1 , 1979 .

[2]  J. Oster,et al.  Infiltration as Influenced by Irrigation Water Quality1 , 1979 .

[3]  J. Oster,et al.  Flocculation Value and Gel Structure of Sodium/Calcium Montmorillonite and Illite Suspensions , 1980 .

[4]  J. D. Rhoades,et al.  Effect of pH on Saturated Hydraulic Conductivity and Soil Dispersion1 , 1984 .

[5]  P. Rengasamy,et al.  Identification of dispersive behaviour and the management of red-brown earths , 1984 .

[6]  Me Sumner,et al.  Sodic soils - New perspectives , 1993 .

[7]  J. Rhoades,et al.  Reduction in hydraulic conductivity in relation to clay dispersion and disaggregation , 1987 .

[8]  R. Naresh,et al.  Field determined hydraulic properties of a sandy loam soil irrigated with various salinity and SAR waters , 1994 .

[9]  David L. Carter,et al.  Saline and sodic soils. Principles-dynamics-modeling. , 1982 .

[10]  J. Rhoades,et al.  Effect of Low Electrolyte Concentration on Clay Dispersion and Hydraulic Conductivity of a Sodic Soil1 , 1981 .

[11]  C. W. Robbins,et al.  A Combined Salt Transport-Chemical Equilibrium Model for Calcareous and Gypsiferous Soils , 1980 .

[12]  J. Quirk,et al.  Chemistry of Saline Soils and Their Physical Properties , 1971 .

[13]  J. Letey,et al.  Response of soils to sodic and saline conditions , 1984 .

[14]  D. Bhumbla,et al.  EFFECT OF SODICITY, pH, ORGANIC MATTER, AND‐CALCIUM CARBONATE ON THE DISPERSION BEHAVIOR OF SOILS , 1984 .

[15]  J. D. Rhoades,et al.  Effects of Clay Type and Content, Exchangeable Sodium Percentage, and Electrolyte Concentration on Clay Dispersion and Soil Hydraulic Conductivity , 1978 .

[16]  R. K. Gupta,et al.  Effect of high salinity and SAR waters on salinization, sodication and yields of pearl-millet and wheat , 1992 .

[17]  J. Rhoades,et al.  Effect of Mineral Weathering on Clay Dispersion and Hydraulic Conductivity of Sodic Soils , 1981 .