Phosphorus sorption isotherm characteristics and availability parameters of Appalachian acidic soils

Abstract

Phosphate (P) sorption isotherms have been widely used to characterize the P status and to establish fertilizer requirements of soils. Recently, mechanistic models have successfully described the nutrient uptake by plants under changing soil and plant parameters. Phosphorus sorption characteristics of eleven representative soils of the Appalachian Region of the United States were evaluated, and experimental P adsorption data were fitted to Temkin, Freundlich, and Langmuir equations to determine the relative importance of the soil parameters in P retention and supply to plant roots. The Barber and Cushman model was used to predict the effect of P fertilization on P uptake by plant. The soils of Appalachia differ considerably with respect to the retention of added P. All three isotherm equations gave good fit with the experimental data and were reliable to describe the P quantity/ intensity relationships of these soils. The following sequence of P adsorption capacity in various soils was established: Tate (BA)? Hayesville (Bt) > Westmoreland (Bt2) ～ Upshur (Btl) ～ Gilpin (A) > Lily (A) ～ Dandridge (E) ～ Watauga (Ap) > Ashe (A) ～ Berks (A) ～ Dekalb (A). In spite of the great differences among soil properties related to surface area and degree of weathering of these soils, the content of free iron (Fe) oxides was the only soil property that correlated with the constants of the isotherm equations. Amounts of P required to give 0.20 μg P/mL varied with soils and were closely related to the constants of the isotherm equations. Soil P parameters from the P adsorption isotherms were used to determine a measure of Cli, b, and De instead of those used conventionally in the Barber and Cushman (1981) model to predict P uptake by corn. Predicted P uptake by corn varied with soils, even at the same P concentration in equilibrium solution (0.20 μg P/mL) or when an equal amount (90 μg P/mL) of P was added to all soils. Predictions of P uptake, however, were not correlated with the amount of P required to give 0.20 μg P/mL in 0.01M CaCl₂ solution or with the constants of the isotherm equations used. Diffusion coefficient and equilibrium P concentration in solution, and two intensity factors, were more important than buffer power in predicting P supplied to roots. These findings may help to explain the lack of significant correlations between the constants of the P isotherm equations and P uptake.     

The specific surface of soils determined by water sorption

The hypothesis that the specific surface of soil can be measured by water sorption is tested with data for 62 subsoils of widely differing origins. Ethylene glycol and water sorption at p/p₀=0.47 are found to be very closely related measurements and both are highly correlated with CEC. Both methods give a satisfactory measure of total specific surface for soils classed as smectitic and having a large CEC. However, the application of the multilayer theory to the sorption of water on external surfaces of clayey soils with small CEC suggests that both sorbates overestimate the specific surface of such soils. A better estimate of the errors would be obtained from isotherm measurements with water, which is more suitable for this purpose than ethylene glycol.     

Prediction of atrazine sorption coefficients in soils using mid-infrared spectroscopy and partial least-squares analysis

This study explored the potential of mid-infrared spectroscopy (MIR) with partial least-squares (PLS) analysis to predict sorption coefficients (Kd) of pesticides in soil. The MIR technique has the advantage of being sensitive to both the content and the chemistry of soil organic matter and mineralogy, the important factors in the sorption of nonionic pesticides. MIR spectra and batch Kd values of atrazine were determined on a set of 31 soil samples as reference data for PLS calibration. The samples, with high variability in soil organic carbon content (SOC), were chosen from 10 southern Australian soil profiles (A1, A2, B, and C in one case). PLS calibrations, developed for the prediction of Kd from the MIR spectra and reference Kd data, were compared with predictions from Koc-based indirect estimation using SOC content. The reference Kd data for the 31 samples ranged from 0.31 to 5.48 L/kg, whereas Koc ranged from 30 to 680 L/kg. Both coefficients generally increased with total SOC content but showed a relatively poor coefficient of determination (R2 = 0.53; P > 0.0001) and a high standard error of prediction (SEP =1.22) for the prediction of Kd from Koc. This poor prediction suggested that total SOC content alone could explain only half of the variation in Kd. In contrast, the regression plot of PLS predicted versus measured Kd resulted in an improved correlation, with R2 = 0.72 ( P > 0.0001) and standard error of cross-validation (SECV) = 0.63 for three PLS factors. With the advantages of MIR-PLS in mind, (i) more accurate prediction of Kd, (ii) an ability to reflect the nature and content of SOC as well as mineralogy, and (iii) high repeatability and throughput, it is proposed that MIR-PLS has the potential for an improved and rapid assessment of pesticide sorption in soils.     

Prediction of wetting front stability in dry field soils using soil and precipitation data

A need exists for information regarding the stability of wetting fronts in field soils because they increase the vulnerability for groundwater contamination. In this study, we develop a simple approach for the evaluation of wetting front stability in dry soils. We show that the stability of wetting fronts in the top layer of a soil depends both on the type of soil and the intensity of the precipitation. Our approach distinguishes stability criteria for wetting events that are different for a high, intermediate, and low infiltration rate. At high infiltration rates, wetting fronts are stable if the infiltration rate exceeds or equals the saturated hydraulic conductivity of the soil. The stability criterion for low infiltration rates (less than approximately 0.2 cm/h for sand soils) is based on two characteristics times[ a gravitational time and an infiltration time. The gravitational time, t_grav, indicates when gravity and capillarity each contribute equally to the process of infiltration. The infiltration time, t_infil, is the duration of the infiltration event. Experimental and literature data show that in well-sorted laboratory sands, wetting fronts are stable when t_infil < 0.002 t_grav. This expression can also be expressed as Wi < 0.002 S² with W the total amount of precipitation, i its intensity, and S the sorptivity at a slightly positive soil-water pressure. For intermediate infiltration rates, wetting fronts remain stable as long as W is smaller than the amount of water needed to wet a distribution layer near the surface. The application of the stability criteria is demonstrated with a case study from the Sevilleta dunes near Socorro, NM.     

抗生素在土壤中的吸附行为研究进展

抗生素是畜禽养殖和水产养殖中常用的一类化学品,其使用量大,体内代谢率低,可通过畜禽粪便的农业施用直接进入土壤环境,在土壤中易残留,富集到一定水平就可能影响生态健康和安全.目前,抗生素污染最令人类担忧的风险是抗性基因和抗性病菌的滋生和传播.抗生素在土壤中的吸附作用是影响其持留、分布、迁移、转化及最终归趋的关键过程.本文选择四环素类、磺胺类、大环内酯类和喹诺酮类4类常用抗生素,论述了pH值、离子强度和金属离子、有机质以及其他土壤理化性质等因素对其吸附的影响,并对抗生素在土壤中的吸附机理进行了初步的探讨.     

Evaluation of arsenite sorption in Spanish soils

Abstract

Arsenite sorption was studied at different temperatures (30,40, and 50°C) to investigate processes that remove arsenite from soil solution (adsorption or precipitation), and if adsorption was taking place, how many sites were involved in this process, and their nature. Adsorption was the only reaction reducing levels of soluble arsenite in the two alkaline soils used in this experiment, Jijona and Agost; however, arsenite precipitation occurred in an acidic substrate (pH 4.0), Galicia soil. Iron (Fe) oxides and clay minerals were the soil components controlling arsenite sorption in the Jijona soil (pH 7.9 and high levels of Fe oxides). Calcite and clay minerals were the inorganic constituents involved in arsenite sorption in the Agost soil (pH 8.0 and high levels of CaCO₃). Arsenite sorption was an endothermic and non‐spontaneous process. The fact that the higher the temperature, the higher the arsenite sorption, however, was likely due to an increase in the diffusion rate.     

Predicting phosphorus sorption isotherm parameters in soil using data of routine laboratory tests

Knowledge of phosphorus(P) sorption dynamics across different soil types could direct agronomic and environmental management of P. The objective of this study was to predict P isotherm parameters for a national soil population using data of routine laboratory tests. Langmuir and Freundlich sorption parameters were calculated from two different ranges(0–25 and 0–50 mg P L~(-1)) using an archive of representative agricultural soil types from Ireland.Multiple linear regression(MLR) identified labile forms of aluminium(Al) and iron(Fe), organic matter(OM), cation exchange capacity(CEC), and clay as significant drivers. Langmuir and Freundlich sorption capacities, Freundlich affinity constant, and Langmuir buffer capacity were predicted reliably, with R~2 of independent validation 0.9. Sorption isotherm parameters were predicted from P sorbed at a single concentration of 50 mg P L~(-1)(S_(50)). An MLR prediction of P sorption maximum in the 0–50 mg P L~(-1) range was achieved, to an accurate standard, using S_(50), OM, and Mehlich-3 Fe(R~2 of independent calibration and validation being 0.91 and 0.95, respectively). Using Giles' four shapes of isotherms(C, L, H, and S), L non-strict-and C-shaped isotherm curves accounted for 64% and 27% of the soils, respectively. Hierarchical clustering identified a separation of isotherm curves influenced by two ranges of Mehlich-3 Al. Soils with a low range of Mehlich-3 Al(2.5–698 mg kg~(-1)) had no incidence of rapid sorption(C shape). Single point indices, Al, or available soil data make the regression approach a feasible way of predicting Langmuir parameters that could be included with standard agronomic soil P testing.     

On the reversibility of phosphate sorption by soils

Sorption of phosphate was induced by incubating phosphate with samples of two soils. Both desorption and further sorption of phosphate were then measured on separate subsamples of the incubated soils. The effects of varying the amount of phosphate incubated with the soil and of period of desorption, or of further sorption, were measured on one soil; the effect of period of incubation was measured on the other. Plots of desorbed phosphate versus concentration were continuous with plots of newly sorbed phosphate versus concentration. Neither of these coincided with the plots of the original additions of phosphate. These results were compatible with a model for the reaction between soil and phosphate in which phosphate is initially adsorbed and subsequently diffuses beneath the adsorbing surfaces. Sorption is reversible in the sense that a continuous curve of sorbed and desorbed phosphate is obtained when these are measured in opposite directions by increasing, or decreasing, the solution concentration of phosphate. However, because dynamic processes are involved, an earlier position of a plot of sorbed phosphate against concentration is not retraced when the concentration is changed.     

Time-dependent sorption of imidacloprid in two different soils

Time-dependent sorption of imidacloprid [1-[(6-chloro-3-pyridinyl)-methyl]-N-nitro-2-imidazolidinimine] was investigated with two German soils (sandy loam and silt loam). Soil batches containing the active ingredient (0.33 mg/kg) were incubated for 100 days. After selected aging periods, imidacloprid desorbed by 0.01 M CaCl(2) (soluble phase) and by organic solvents (methanol and acetonitrile) and reflux extraction with acidified methanol (sorbed phase) was determined. Calculated sorption coefficients K(d) and K(oc) increased by a factor of 3.2-3.8 during 100 days of aging. Additionally, the time-dependent sorption was verified by a column leaching experiment with the aged soil. The amount of imidacloprid in column eluates (0.01 M CaCl(2)) decreased compared to total recovered by a factor of approximately 2. Sorption of imidacloprid thus increased with residence time in soil, making it more resistant to leaching. These results are further information to explain the low leaching potential of imidacloprid in the field, despite its high water solubility.     

Phosphate sorption in some representative soils of Bangladesh

An experiment was conducted to observe the phosphate sorption potential of some soils of Bangladesh. Three soil series of calcareous origin, namely Sara (Aquic Eutrochrept), Gopalpur (Aquic Eutrochrept) and Ishurdi (Aeric Haplaquept), and two soil series of non-calcareous origin, namely Tejgaon (Rhodic Paleustult) and Ghatail (Aeric Haplaquept), were selected. The soils were equilibrated with dilute solution of calcium chloride containing graded concentrations of phosphate (0, 1, 2, 5, 10, 25 and 50?μg?P?mL^?1), and the amount of phosphate sorbed or desorbed was determined. Although all the soils showed potential for sorbing phosphate from applied phosphorus, their ability to sorb phosphorus differed. Increasing rates of phosphate application increased the amount of P sorption but reduced phosphate sorption percentage in all soils except Tejgaon. Phosphate was sorbed by the soils in the order: Tejgaon > Ghatail > Ishurdi > Gopalpur > Sara at 50?μg?P?mL^?1 application. Soils possessing higher amounts of free iron oxide and clay sorbed more phosphate from applied phosphorus.     

Estimation of the phosphorus sorption capacity of acidic soils in Ireland

The test for the degree of phosphorus (P) saturation (DPS) of soils is used in northwest Europe to estimate the potential of P loss from soil to water. It expresses the historic sorption of P by soil as a percentage of the soil's P sorption capacity (PSC), which is taken to be α (Al_ox + Fe_ox), where Al_ox and Fe_ox are the amounts of aluminium and iron extracted by a single extraction of oxalate. All quantities are measured as mmol kg soil^?1, and a value of 0.5 is commonly used for the scaling factor α in this equation. Historic or previously sorbed P is taken to be the quantity of P extracted by oxalate (P_ox) so that DPS = P_ox/PSC. The relation between PSC and Al_ox, Fe_ox and P_ox was determined for 37 soil samples from Northern Ireland with relatively large clay and organic matter contents. Sorption of P, measured over 252 days, was strongly correlated with the amounts of Al_ox and Fe_ox extracted, but there was also a negative correlation with P_ox. When PSC was calculated as the sum of the measured sorption after 252 days and P_ox, the multiple regression of PSC on Al_ox and Fe_ox gave the equation PSC = 36.6 + 0.61 Al_ox+ 0.31 Fe_ox with a coefficient of determination (R²) of 0.92. The regression intercept of 36.6 was significantly greater than zero. The 95% confidence limits for the regression coefficients of Al_ox and Fe_ox did not overlap, indicating a significantly larger regression coefficient of P sorption on Al_ox than on Fe_ox. When loss on ignition was employed as an additional variable in the multiple regression of PSC on Al_ox and Fe_ox, it was positively correlated with PSC. Although the regression coefficient for loss on ignition was statistically significant (P < 0.001), the impact of this variable was small as its inclusion in the multiple regression increased R² by only 0.028. Values of P sorption measured over 252 days were on average 2.75 (range 2.0–3.8) times greater than an overnight index of P sorption. Measures of DPS were less well correlated with water‐soluble P than either the Olsen or Morgan tests for P in soil.     

Phosphorus sorption kinetics in different types of alkaline soils

This study investigated phosphorus sorption kinetics of three different soils from three sites within the Sahel region of Tunisia; iso-humic soils from Chott-Mariem site, calcic-magnesic soils from Enfidha site and saline-sodic soils from Kondar site. Soils from all sites were sampled (0–25 cm) and analysed for their physico-chemical proprieties. In previous works, we determined the adsorption efficiency of these different soils. In this study, we focused on the influence of contact time on phosphorus adsorption by the different soils. The analytic data were approached from the following kinetics models: pseudo-first-order, pseudo- second-order and Elovich model. The second order model was shown to be the best fit for describing phosphorus adsorption by each soil sample, as seen from the correlation coefficient R² which ranged from 0.68 to 0.96 for the pseudo-first-order model, 0.91 to 0.99 for pseudo-second-order model and 0.84 to 0.94 for Elovich model.     

Degradation and sorption of pirimiphos-methyl in two Nigerian soils

This research is a continuation of a study on the behavior of hydrophobic organic compounds in the environment and describes the simultaneous abiotic degradation and sorption of pirimiphos-methyl (O-2-diethylamino-6-methylpyrimidin-4-yl O,O-dimethylphosphorothioate) under controlled conditions in soil/water slurries. A microfiltration-HPLC technique was employed to follow these processes in two well-characterized soils from the Middle Belt region of Nigeria. Rapid sorption of the pesticide occurs during the first 10 min of equilibration and accounted for 37% of the original pirimiphos-methyl in the Rhodic Kandiustalf soil and for 41% of the original concentration in Aquic Ustropept soil. Subsequent slow processes were followed during the remaining 30 days of the experiment. During this time, first-order rate constants for disappearance from solution of pirimiphos-methyl were found to have values of 6.1 x 10(-)(7) and 9.8 x 10(-)(7) s(-)(1) for the Rhodic and Aquic soils, respectively. Similarly, rate constants for production of the product, pyrimidinol, were calculated to be 6.0 x 10(-)(7) and 9.4 x 10(-)(7) s(-)(1) for the Rhodic and Aquic soils, respectively, giving pesticide degradation half-lives of 13 and 8.5 days. Disappearance of the pesticide is discussed in terms of a scheme involving both sorptive uptake by the soil and degradation by hydrolysis in the presence of the soil matrix. The labile sorption capacities for pirimiphos-methyl in the Rhodic and Aquic soils were found to be 0.75 and 0.90 micromol g(-)(1), respectively.     

Kinetics of arsenite sorption and desorption in Spanish soils

Abstract

The arsenite (AsO₂ ^‐) sorption and desorption by three Spanish soils were investigated. An Elovich type equation and a modified Freundlich equation were used to describe the kinetics of arsenic [As (III)] sorption and desorption rates. In both cases, the Elovich equation proved to be superior when correlation coefficients were considered. Arsenic (III) sorption and desorption rate increases as the As concentration in the original solution increases. Arsenite sorption was reversible for the soils, initial concentrations, and reaction times used in this study.     

The analysis of isotherm data to describe polyfunctional exchangers and soils

The analysis of isotherms of cation ion-exchange adsorption in heterogeneous polyfunctional ion-exchangers and soils containing groups of adsorption centres non-equivalent in their preference for exchanging cations permits calculation on the basis of experimental data of the selectivity coefficients ($\text{K}{}_{\mathrm{<mtext>i</mtext>}}$) and maximum adsorption of cations ($\text{S}{}_{\mathrm{<mtext>i</mtext>}}$) for each individual group of heterogeneous centres and thus provides an expression for the exchange isotherm with stable values of $\text{K}{}_{\mathrm{<mtext>i</mtext>}}$ over a wide range of concentrations. A method based on a step-by-step breakdown of the experimental isotherm of ionexchange adsorption was used to describe Ca²⁺ and Pb²⁺ exchange in samples of a leached chernozemic soil. The data obtained demonstrated existence of two groups of non-equivalent adsorption centres. Theoretical and experimental data were found to be in sufficient agreement.     

原状土与扰动土导气率、导水率与含水率的关系

为分析土壤导气特性与土壤导水特性间的关系,该文通过研究陕西杨凌小麦试验田士样导水率和导气率随含水率的变化特征,比较原状土与扰动土导气和导水特征,分析相对导水率和相对导气率与饱和度的关系,结果发现导水率随含水率的增加而减小,且无论导水率还是导气率原状土都比扰动土大,证实土壤结构及孔隙特征对水和气的传输有巨大的影响,扰动土和原状土变化趋势虽然基本相同,但曲线不重合,说明扰动土和原状土的孔隙连接性和弯曲程度不尽相同.