Sources of soluble calcium and magnesium and their effects on sodium adsorption ratios of solutions in two soils of israel

Exchange reactions and dissolution of soil minerals in 0.01, 0.05 and 0.1 N NaCl solutions at three different times of contact between two soils and the solutions were studied. It was found that dissolution of soil minerals occurred continuously and the release of divalent cations from exchange sites did not stop the process. The amounts dissolved from both soils increased as the concentration of NaCl and time of contact increased. The minimum amounts of calcium and magnesium dissolved in 0.01 N NaCl during 10 min of contact between soil and solution were 0.7 and 0.9 mequiv./100 g from a noncalcareous terra rossa and a calcareous grumusol, and the maximum amounts of these cations dissolved in 0.1 N NaCl during two weeks of contact were 2.5 and 3.1 mequiv./100 g soil from the terra rossa and grumusol, respectively. The amounts released from exchange sites were proportional to the cation exchange capacities of the soils and the SAR of the soil solutions. The effects of calcium and magnesium released from dissolution of soil carbonates and aluminosilicate and from exchange sites on SAR of soil extracts were investigated.     

Reclamation of saline‐sodic soil under a rice–wheat system by horizontal surface flushing

Saline sodic soil with a high content of soluble carbonates is one of the important agricultural soils on the Central Indo‐Gangetic plains and elsewhere. Conventional reclamation procedures using gypsum application followed by vertical leaching (GC) is uneconomic; high ECe and precipitation of applied gypsum, reacting with soluble carbonates, reduce the efficacy of gypsum in these soils. This paper reports results from a project designed to evaluate reclamation by irrigation of the ploughed soil and turning of soil with a power tiller followed by flushing of standing water after 24 h, a second flushing after 7 days and subsequent application of gypsum and vertical leaching (GF2). Average rice and wheat production after GF2 significantly increased (25 and 62%, respectively) over the conventional practice. Compared with conventional treatment, GF2 significantly reduced the ECe and SAR of the soil and improved physical properties such as ζ‐potential, dispersible clay content, water stable aggregates expressed as MWD, and saturated hydraulic conductivity. Split application of gypsum between flushing (GF1/2 and GF2/3) gave similar results to GF2 in terms of soil amelioration and crop production.     

Hydraulic conductivity of calcareous soils as affected by salinity and sodicity. II. effect of gypsum application and flow rate of leaching solution

Abstract

Saline‐sodic irrigation water, coupled with low annual rainfall and high evapotranspiration in the arid and semi‐arid regions have resulted in accumulation of soluble salts in the soil solution and of cations (especially sodium ions) on exchange sites, which can alter the structure and, consequently, affect the soil hydraulic conductivity (HC). Among the different factors, the amount of gypsum applied and the flow rate of leaching solution are major factors influencing the HC of the soil in the presence of saline sodic solutions. The study was initiated to improve the understanding of swelling and dispersion processes (as two major mechanisms responsible for reduction in HC) in response to saline‐sodic conditions, in particular, the role of gypsum application and the flow rate of leaching solutions. The study was conducted in a series of two leaching experiments. In the first set, different rates of gypsum (i.e., 0, 10, 20, and 30 tons ha^‐1) were mixed with 4 soil samples and leached with a saline‐sodic solution of concentration of 100 meq (NaCl+CaCl₂)L^‐1 with sodium adsorption ratio (SAR) 20 and the base flow rate (BFR) of 15 mL min^‐1. In the second set of experiments, the same soils treated with the same gypsum level and the same leaching solutions as in the first set, but leached with the BFR of 5 mL min^‐1 instead of the BFR of 15 mL min^‐1. In general, the gypsum application modified the suppressing effect of salinity and sodicity on the HC values of the tested soils, and the effects were more pronounced for higher rates of gypsum applied. However, increase in the BFR from 5 to 15 mL min^‐1, significantly masked this recovering effect of gypsum application, and the effect was reflected in both swelling and dispersion processes.     

Downward Movement of Soil Cations in Highly Weathered Soils Caused by Addition of Gypsum

Abstract

Besides supplying calcium (Ca) and sulfur (S) to plants, gypsum has recently been used in agriculture to ameliorate some soil physical and chemical properties, especially to alleviate aluminum phytotoxicity in subsoils. When applied in large quantities, however, gypsum may leach significant amounts of nutrients from the plow layer. This study was conducted to assess the effect of gypsum addition to the soil on the magnitude of cation leaching as well as the relationship of leaching with some soil properties in a group of seven Brazilian soils. Rates of gypsum equivalents to 0, 5.0, 10, and 20 t ha^?1 (0, 2.5, 5.0, and 10 g kg^?1) were mixed with triplicate soil samples consisting of 3.0 kg of dry base soil. After 60 days of incubation at room temperature (15–25°C), the experimental units were packed into polyvinyl chloride leaching columns (32‐cm‐high×10 -cm-diameter) at a density of 0.9 g cm^?3. Thereafter, they were percolated once a week with a volume of distilled water equivalent to 1.5 times the total soil porosity over 11 weeks. Soil samples were collected before the first and after the last percolation, for chemical analysis. Averaged across soils, 11 percolation events leached about 26% of each Ca, magnesium (Mg), and potassium (K) from the treatment without gypsum. Averaged across soils and rates, addition of gypsum leached 41–94% of added Ca, 13–90% of exchangeable Mg, and 13–58% of exchangeable K, and the highest losses occurred on the sandiest soils. The relationship between soil parameters and Ca leaching varied with gypsum rate: in the treatments that received gypsum, leaching was negatively related to cation exchange capacity (CEC), clay, and organic matter, and positively correlated with sand; in the treatment with no gypsum, leaching correlated with the same parameters above, nevertheless, all coefficients presented opposite signs. Leaching of K caused by gypsum was negatively associated with clay and positively with sand, whereas leaching of Mg was poorly correlated with any soil parameter. Gypsum is a good source to promote high and fast downward movement of Ca in the soil profile, but rates must be cautiously chosen because of excessive leaching of Mg especially on soils with low CEC.     

Gypsic pedofeatures and elementary pedogenetic processes of their formation

Elementary pedogenetic processes forming gypsic pedofeatures in gypsiferous soils are discussed. Several groups of such processes are distinguished: (1) weathering of gypsum-bearing rocks; (2) gypsum formation associated with weathering of sulfuric (pyritic) rocks; (3) precipitation of gypsum owing to the inflow of soil solutions saturated with Ca and SO₄ and their evaporative concentration; (4) gypsum formation owing to exchange reactions in soils between calcium in the exchange complex and sodium sulfate solutions; (5) gypsum formation upon interaction of calcium carbonates with sodium sulfate water resulting in the loss of CaCO₃ and gypsum accumulation (decalcification process); (6) colluvial and alluvial redeposition of gypsum in the landscape with its accumulation in the subordinate positions, where gypsiferous soils are formed; and (7) eolian deposition of gypsum on the soil surface with the formation of gypsum-bearing horizons. The micromorphological specificity of the gypsic pedofeatures reflects the processes of their destruction and/or accumulation in the soil profiles. It is shown that gypsum accumulation in soils is a pedogeochemical process that manifests itself in different natural zones upon the presence of gypsum sources.     

Improvement of saline soils through indigenous materials

Reclamation of saline soils involves heavy leaching with water, with or without the addition of gypsum, depending upon the calcium content of the soil. Many a time, flushing the soil becomes difficult because of its low permeability due to high clay content, as obtained in most of the coastal saline soils of India. There is also the danger of hydrolysis under conditions of prolonged leaching, which may result in raising the pH, dispersion of the soil, impeded drainage, root penetration and aeration. Reclamation of such soils, therefore, calls for the improvement of physical conditions for better permeability and addition of calcium rich substances. Indigenous materials like basic slag, lime sludge, calcareous soil and iron rich mineral soil, in addition to gypsum, may serve as useful amendments for improving the soil's physical conditions. It was, therefore, thought worth-while to study the effect of addition of these materials on the improvement of saline soils.     

LEACHING OF EUPHRATES SALINE SOIL IN LYSIMETERS

A saline soil from Euphrates alluvium at Abu-Ghraib was leached in two lysimeters with river water and the changes in composition of the soils and of the leachates were measured as well as the hydraulic conductivity. The results show that the presence of gypsum prevents the soils becoming sodic as leaching with irrigation water of favourable composition proceeds.     

Salt composition of groundwater and reclaimed solonetzes in the Baraba Lowland

Solonetzes of experimental trials established in 1981 and 1986 in the Baraba Lowland were examined. It was found that gypsum-based ameliorants improve the soil and lead to a decrease in the content of soluble salts in the soil profile. Exchange processes between cations of the soil adsorption complex and calcium of gypsum were particularly intensive in the first years after gypsum application. This resulted in a sharp rise in the content of soluble salts that migrated down the soil profile to the groundwater. In the following years, the reclaimed solonetzes were desalinized under the conditions of relatively stable groundwater level. On the 30th year after single gypsum application, the groundwater level sharply rose (to 50 cm), and the soil was subjected to the secondary salinization; the contents of bicarbonates, carbonates, and sodium in the soils increased. Spring leaching caused some desalinization, but the content of soluble salts in the upper soil meter increased again in the fall. A close correlation between the salt compositions of the groundwater and the reclaimed solonetzes was revealed.     

Modern and paleolimnological evidence for accelerated leaching and metal accumulation in soils in New England,caused by atmospheric deposition

Empirical field evidence for changing chemical processes in soils caused by atmospheric deposition of pollutants consists of: (1) Long-term water quality data including total dissolved solids, concentrations of specific metals (e.g. Ca), and conductivity; (2) Cation exchange capacity and base saturation values for soils located on precipitation pH gradients; (3) Lysimeter studies; and (4) Chemical analysis of organic soils on precipitation pH and metal gradients. For well-drained organic soils, as precipitation pH decreases, metals are differentially leached at an accelerated rate (Mn>Ca>Mg≥Zn>Cd and Na>Al). Experimental field and laboratory lysimeter studies on soil columns yield similar results, with increases in leaching rates for soil solutions with pH=3 up to 100 × values for soil solutions with pH=5. Nearly 100% of the Pb from precipitation is accumulating in the organic soil layer or sediments. Zn is accumulating in soils and sediments where the pH's of precipitation, soil solutions, and surface waters are generally above 5 to 5.5. At lower pH values Zn and other chemically similar elements are desorbed/leached (net) at an accelerated rate. Chemical analyses of dated sediment cores from high and low altitude lakes, with drainage basins relatively undisturbed for the last 200+ yr, reveal that increased deposition of metals on a regional scale started in the northeastern United States as early as 1880, consistent with increased fossil fuel consumption. This suggests acidified precipitation as early as 1880. Cores from historically acidified lakes (pH<≈5.3 to 5.5) indicate that, as acidification of surface waters occurs (caused by acidic deposition), concentrations of Zn, Mn, and Ca decrease in the sediment. Apparently the metals are leached from the detritus prior to sedimentation. This conclusion results from data from experimental acidification of sediment cores and the general observation that precipitation pH is generally ≥0.5 pH units lower than lake water pH. Accelerated leaching of soil in New England dates to earlier than 1900.     

Liming effect on dissolved organic matter leaching

The main agrochemical treatment applied in agriculture to lower harmful soil acidity is liming. Long term studies showed that application of calcium carbonate fertilizer brought about higher leaching of dissolved organic matter (DOM) in pot, lysdmetric and field experiments. Outflows obtained from limed soils contained 44.8% more DOM in comparison with nonlimed soils. During four years of lysimetric experiments it was found that the amounts of DOM from limed soils were increased by 52.7%. In the field experiments the amounts leached from one hectare of limed and nonlimed soil ranged 25.6 kg and 19.2 kg per year, respectively. DOM leached from limed soils was characterized by higher (45.4%) contents of carboxylic groups and humic substances (19.7%). Dissolved organic substances particularly humus rich in functional groups, due their complexing properties bound plant nutrients leached from soils and modify geochemical mobility of metals and anions. Therefore, DOM can play a significant role in the migration of chemical substances in agriculture landscape.     

Leaching of zinc,lead and cadmium in columns of calcareous soils

Leaching of zinc, lead and cadmium was studied in columns packed with soil differing in pH, clay, organic matter and calcium carbonate contents. Distribution of 1 N HCI extractable heavy metals in different layers of the columns as a function of the amount of water leached was the criteria for measuring leachability of the three metals. Leachates contained only traces of the metals. Movement of surface applied metals could be observed only upto 30mm depth. Cadmium, which was observed to be the most mobile element, was leached to a depth of 30–40mm in a pH 7.5, light textured soil with 0.9 % calcium carbonate. Presence of superphosphate at the soil surface reduced the extent of leaching to an appreciable extent.     

Effects of drying and wetting on extractable aluminum in strongly acid soils and in aluminum-saturated clays

A number of field-moist strongly acid soils, NaObr-treated soils, and Al-saturated clays were subjected to drying and wetting treatments in the laboratory. Oven drying of samples resulted in decreases in extractable Al and increases in extractable H from field-moist soils containing more than 12 mequiv./100 g exchange acidity and from Al-saturated clays, and wetting the samples resulted in the reverse. However, when field-moist soil samples containing less than 7 mequiv./100 g exchange acidity were oven dried, both the extractable Al and extractable H tended to increase. Removing organic matter with NaOBr from a soil sample low in exchange acidity resulted in a change from an increase to a decrease in extractable Al upon oven drying. In all cases, the extractable Al and extractable H contents fluctuated cyclically with repeated drying and wetting. The cause for the observed changes was attributed to Al hydrolysis, with additional influence from soil acidity buffering, Al interlayer formation, and inorganic and organic matter dissolution.     

Adsorption controls mobilization of colloids and leaching of dissolved phosphorus

Loss of phosphorus (P) from agriculture contributes to the eutrophication of surface waters. We have assessed the magnitude and controls of P leaching and the risk of colloid‐facilitated transport of P from sandy soils in Münster. Concentrations of soluble reactive P in drainage water and groundwater were monitored from 0.9 to 35 m depth. Total P concentrations, P saturation, and P sorption isotherms of soil samples were determined. Concentrations of dispersible soil P and colloidal P in drainage water and groundwater were investigated. The concentrations of soluble reactive P in drainage water and groundwater were close to background concentrations (< 20 µg P l^?1). Median concentrations in excess of 100 µg P l^?1 were found down to 5.6 m depth at one of four research sites and in the lower part of the aquifer. Experimentally determined equilibrium concentrations and the degree of P saturation were good predictors of P concentrations of drainage water. Large concentrations of dispersible P were released from soil with large concentrations of oxalate‐extractable P and addition of P induced further dispersion. Colloidal P was transported in a P‐rich subsoil when there was a large flow of water and after nitrate had been flushed from the soil profile and total solute concentrations were small. We conclude that the concentration of soluble reactive P in drainage water is controlled by rapid adsorption in the sandy soils. Subsurface transport of dissolved P contributes substantially to the loss of P from the soils we investigated. Accumulation of P in soils increases the risk of colloid‐facilitated leaching of P.     

Distribution patterns of soluble salts and gypsum in soils under large-scale irrigation agriculture in Central Asia

Abstract

Soil salinization is a serious problem in the arid and semi-arid regions of Central Asia. To address the problems, we analyzed the dynamics and distribution patterns of salts in both rice-based and cotton-based cropping fields in selected farms of southern Kazakhstan and Uzbekistan with special emphasis on the dynamics of gypsum, which had a lower solubility than Na salts, as an index of water-movement regimes in irrigated fields. Most of the rice-based plots and some of the cotton-based plots exhibited no surface accumulation of soluble salts or gypsum because of repeated washing by a huge amount of irrigation water in the former or comfortable drainage in the latter. These soils are probably free from the risk of secondary salinization under present conditions and management practices. In contrast, uncultivated plots near canals accumulate both soluble salts and gypsum in the surface soil layers, and these salts would not be leached out without a drastic change to a predominantly downward pattern of water movement. In the intermediate stages in terms of soil salinization, some soils accumulated substantial amounts of soluble salts in surface layers but relatively low amounts of gypsum. In this case, periodic irrigation could have washed out most of the gypsum and soluble salts in a downward direction and, consequently, it is possible to leach out the accumulated soluble salts by applying additional irrigation water if necessary. However, there were some cases in which soils accumulated large amounts of gypsum in surface layers as well as soluble salts, suggesting that irrigation/drainage is generally insufficient to remove gypsum with a lower solubility and that these profiles are dominated by an overall upward movement of water. For these soils, drainage facilities should be improved to ensure the efficient leaching of accumulated salts on cropping. Thus, the condition of irrigated plots in terms of the direction of water movement and resulting salt regimes can be well understood from the distribution patterns of both soluble salts (or cations) and gypsum.     

Amendment of drilling fluid-affected soils with calcium salts

Land disposal of waste drilling fluid is an environmental concern because of the high salt content and the presence of potential toxic elements. A water-based drilling fluid was tested in a laboratory column study to determine the feasibility of leaching excessive salt without mobilizing chromium (Cr). The drilling fluid-affected two Alfisols with similar mineralogy, acidity, and texture were treated with gypsum (CaSO₄ · 2H₂O), calcium carbonate (CaCO₃), or calcium phosphate (CaHPO₄) (0 to 2% of weight). The electrical conductivity (EC) increased and the sodium adsorption ratio (SAR) decreased with increasing Ca-salt concentration. The pH did not vary significantly with the changes in the concentrations of gypsum and calcium phosphate. The pH of the mixtures increased in proportion to the concentration of added calcium carbonate. The hydraulic conductivity increased and the mobility of the soil particles decreased with increasing Ca-salt concentration. The Cr mobility decreased by gypsum and CaCO₃ treatments but it increased by calcium phosphate treatment. The soil with a higher content of organic matter and cation exchange capacity (CEC) showed a higher hydraulic conductivity and lower Cr mobility than the other soils at the same levels of the treatment. The results of this study suggest that the amendment of drilling fluid-affected soils with CaCO₃ and gypsum can enhance the leaching of excessive salt and reduce the Cr mobility. Among loamy soil, those with a higher CEC and organic matter content are more suitable for land disposal of drilling fluid.     

土壤中水溶性铜对西红柿的毒害影响因素及预测模型

该文选取17种具有代表性的中国土壤,研究了土壤孔隙水以及0.01mol/LCaCl2浸提态Cu对西红柿生长的毒害,结果发现对于土壤孔隙水中Cu对西红柿生物量10%抑制的毒性阈值(EC10)和50%抑制的毒性阈值(EC50),在17个非淋洗土壤中变化范围分别为0.06～1.47和0.17～3.42mg/L,淋洗土壤变化范围分别为0.05～2.24和0.13～4.37mg/L,最大值与最小值相差为23～41倍;0.01mol/LCaCl2提取态Cu的EC10和EC50,在非淋洗土壤变化范围分别为0.18～2.64和0.57～6.14mg/kg,淋洗土壤变化范围分别为0.18～1.28和0.61～7.11mg/kg,相差从6.9～14.4倍,表明土壤溶液性质影响水溶性Cu对西红柿的毒性阈值。同时,发现土壤孔隙水中Ca2+、溶解性有机碳是影响孔隙水中Cu对西红柿生长毒性的主要因子。当进一步考虑土壤溶液的重要因子(溶解性有机碳、土壤溶液pH值、电导率、全硫含量、Ca2+、Mg2+、K+、Na+),发现基于水溶性Cu的毒性阈值和土壤溶液性质的多元回归系数变化范围为0.75～0.99,说明利用土壤溶液性质能较好的预测土壤中水溶性Cu对西红柿的毒性阈值。该研究可为土壤水溶性Cu的风险评估提供参考。     

PRECIPITATION OF CARBONATES IN SOILS IN CONTACT WITH WATERS UNDERSATURATED OR OVERSATURATED IN RESPECT TO CALCITE*

Under transient conditions, the precipitation of carbonates in a calcareous and a non-calcareous soil was influenced by calcium, magnesium and bicarbonate ions from soil sources. These sources were: the soil solution, the soil exchange complex and the dissolution of aluminosilicates. There was no significant difference between the amount of carbonates which precipitated in the two soils when in contact with the same water. It was found that for small portions of water in contact with the two soils, precipitation of carbonates took place both from under-saturated and the over-saturated waters. As the cumulative amounts of water in contact with the soils increased, the amount of ions contributed by the residual soil solutions and the exchange complexes decreased, and the amount of precipitating carbonates decreased also. At very large cumulative amounts of water, the precipitation of carbonates in the soils was controlled by both the water and the ions released from the soils.     

天山荒漠景观内蒸发地球化学垒的研究

天山荒漠景观内的蒸发地球化学垒可分为碳酸盐蒸发垒、石膏蒸发垒和易溶盐蒸发垒。这些蒸发垒沿天山山脉呈带状分布 ,自天山山脉至两侧盆地依次分布碳酸盐蒸发垒、石膏蒸发垒和易溶盐蒸发垒。土壤中碳酸盐的积聚导致Mn、Ti、Fe、V、Sc、Cu、Co和B等元素含量的降低。石膏的富集常伴随着土壤中B和Sr含量的增加。随易溶盐的大量积累 ,元素B的聚集非常明显 ,而Mn、Fe、Ti、V、K、Ba、Li、F和Zn等元素含量则明显降低。蒸发地球化学垒对元素的生物有效性也有较明显的影响。碳酸盐的积累明显减低了Fe、Cu、B等元素的生物有效性 ,F元素在碳酸盐蒸发垒内CO2 -3 和HCO-3 含量较高的土壤中生物有效性较高。在易溶盐蒸发垒内元素B有较强的生物有效性     

黄土的连续提取实验及Rb/Sr值意义

通过连续提取实验 ,将黄土和古土壤中元素的赋存状态分成六种形态 :水可溶态、可交换态、碳酸盐结合态、铁锰氧化物结合态、有机物结合态和残留态。结果表明 ,K和Rb等元素 ,主要赋存于残留态中 ,而Ca、Sr等元素主要赋存于碳酸盐结合态和残留态中。Sr在黄土和古土壤中的赋存状态明显与Ca的分布有关。在风化成壤作用中 ,碳酸盐的淋溶和含Ca硅酸盐矿物的分解 ,引起Sr的淋失 ,而Rb保持稳定。因此 ,Rb Sr值指示了黄土和古土壤遭受的淋溶程度 ,反映了黄土高原的降雨量 ,是夏季风强度变化的替代性指标     

Organic and Inorganic Amendments Affect Soil Concentration and Accumulation of Cadmium and Lead in Wheat in Calcareous Alkaline Soils

Irrigation with untreated effluent in periurban agriculture could result in accumulation and bioconcentrations of cadmium (Cd) and lead (Pb). Different amendments were used to investigate their effect on availability, concentration, and uptake of metals by wheat in texturally different soils. Crop was irrigated with water containing Cd and Pb at 20 mg L^?1, thereby adding 260 mg pot^?1 of each metal. Amendments included calcium carbonate at 6 or 12%, gypsum at 50 or 100% of the soil gypsum requirement, farm manure at 7.50 or 15.00 g kg^?1 soil, and a control. Amendments decreased ammonium bicarbonate diethylenetriaminepentaacetic acid (AB-DTPA)–extractable Cd and Pb concentrations and uptake by wheat. Dry matter, concentration, uptake, and extractability of Cd and Pb were greater in sandy loam soil compared with those in sandy clay loam soil irrespective of amendments. Sequential extraction showed that more metals were extracted from the control in all fractions and that predominantly metals were found in the carbonate fraction.