Using chemical analysis and modeling to enhance the understanding of soil solution of some calcareous soils

2012 ◽  
Vol 68 (7) ◽  
pp. 2041-2049 ◽  
Author(s):  
Mohsen Jalali
Soil Research ◽  
1997 ◽  
Vol 35 (2) ◽  
pp. 227 ◽  
Author(s):  
I. C. R. Holford

Phosphorus (P) is the most important nutrient element (after nitrogen) limiting agricultural production in most regions of the world. It is extremely chemically reactive, and more than 170 phosphate minerals have been identified. In all its natural forms, including organic forms, P is very stable or insoluble, and only a very small proportion exists in the soil solution at any one time. Plant-available P may be considered in either its quantitative or intensive dimension. The quantity of available P is time-specific and crop-specific, because it is the amount of P that will come into the soil solution and be taken up by the crop during its life cycle. The intensity of available P (availability) is most easily identified with its concentration in the soil solution. The soil property controlling the relationship between the solid phase P and its concentration in solution is known as the buffering capacity. The solid phase P involved in this relationship is only a small proportion of the total P, and is known as labile P. It is usually measured by isotopic exchange, but this exchangeable P component does not include the sparingly soluble compounds that also replenish the soil solution as its concentration is depleted by plant uptake. The buffering capacity is the ability of the soil solution to resist a change in its P concentration as P is removed by plant uptake or added in fertilisers or organic materials. Buffering capacity is synonymous with sorptivity, which is a preferable term in the context of the reactivity of P fertiliser with soil. It is usually measured from an adsorption isotherm. By fitting a suitable equation, such as the Langmuir, the total sorption capacity as well as the sorption strength can be determined. Both parameters are important in understanding P availability in soils. Buffering capacity has a major effect on the uptake of labile P because it is inversely related to the ease of desorption of solid phase P and its diffusion. Available P therefore is a direct function of the quantity of labile P and an inverse function of buffering capacity. This has been demonstrated in plant uptake studies. Similarly, the most effective methods of measuring available P (soil tests) are those which remove a proportion of labile P that is inversely related to buffer capacity. Soil tests which measure the concentration of P in solution actually measure availability rather than available P, and their efficacy on a range of soils will depend on the uniformity of the soils" buffer capacities. The most effective soil test usually consists of an anionic extractant. Acidic lactate or fluoride have been found most effective in New South Wales, on a wide range of soils, except calcareous soils which neutralise the acidic component (usually hydrochloric or acetic acid) of the extractant. Sodium bicarbonate (pH 8 · 5) has been found effective on calcareous soils and is widely used throughout the world. It has proved unreliable on NSW soils, and may need more thorough evaluation on non-calcareous soils in other parts of Australia.


2019 ◽  
Vol 28 (1) ◽  
pp. 93-110
Author(s):  
Tasmeena Sultana Yousuf ◽  
Mohammad Enayet Hossain ◽  
Mohammad Zafar Afsar ◽  
Khan Towhid Osman

An experiment was carried out to study the effects of calcareousness on phosphate sorption indices of soils using three representative calcareous soils, namely Sara (Aquic Eutrochrept), Gopalpur (Aquic Eutrochrept), and Ishurdi (Aeric Haplaquept) series of Bangladesh. Three non-calcareous soils, namely Belabo (Typic dystrudepts), Sonatala (Aeric Endoaquepts) and Ghatail (Aeric Haplaquept) series were also selected for comparison purposes. Phosphate sorption indices of soils were calculated using Langmuir and Freundlich isotherms. Isotherms were constructed taking one gram of air-dried sieved (< 2 mm) soil into a 50 ml centrifuge tube, and subsequently adding seven initial P concentrations, namely 0, 1, 10, 25, 50, 100 and 150 μg/ml to each centrifuge tube employing a soil/solution ratio of 1 : 20 (w/v). According to the Langmuir equation, the amount of phosphate sorbed followed the order: Sonatala > Ghatail > Sara = Gopalpur > Ishurdi > Belabo. The abundance of amorphous iron rather than the calcareousness was putatively responsible for the high phosphate sorption capacity of soils. Maximum phosphorus buffering capacity (MPBC) of the calcareous soils ranged from 33.4 - 62.8 l/kg. Langmuir and Freundlich equations produced different values for soil P requirements (SPR) at 0.2 and 1.0 mg P/l. Calcareous soils would require 27 - 44 mg P/kg soil to attain 0.2 mg P/l soil solution, which is deemed sufficient for crop growth. The soils would require 32 - 58 mg P/kg soil to reach 1.0 mg P/l soil solution, which is regarded to be safe for soils in terms of susceptibility to P losses. The calculated Langmuir constant b values were higher than the threshold value of 0.07 l/mg for two of the calcareous soils. Therefore, even though the non-calcareous soils sorbed more phosphate, higher bonding energy of P sorption for calcareous soils makes them less vulnerable to loss via surface runoff. Dhaka Univ. J. Biol. Sci. 28(1): 93-110, 2019 (January)


1969 ◽  
Vol 49 (3) ◽  
pp. 305-312 ◽  
Author(s):  
E. T. Lewis ◽  
G. J. Racz

The extent of movement of phosphorus from the application site of P-32 labelled monoammonium phosphate and diammonium phosphate pellets was investigated. The rate of movement of phosphorus from a monoammonium phosphate pellet was also studied. The extent of phosphorus movement from a monoamnionium phosphate pellet was greater than that from a diammonium phosphate pellet. This observation was more noticeable in the calcareous soils than in the noncalcareous soils. The extent of phosphorus movement was greater in noncalcareous soils than in calcareous soils for both sources of phosphorus when added as a pellet. The rate of movement of phosphorus was also more rapid in noncalcareous soils than in calcareous soils.It is most likely that the high pH and large amounts of calcium and magnesium found in the soil solutions of the calcareous soils resulted in a rapid precipitation of the added phosphorus very close to the pellet site. Thus, the rate and extent of phosphorus movement in the calcareous soils was restricted more than in the noncalcareous soils, which had a lower pH and contained smaller amounts of calcium and magnesium in the soil solution.


1961 ◽  
Vol 9 (2) ◽  
pp. 108-117
Author(s):  
H. Broeshart ◽  
J.G. Van Schouwenburg

The effect of development stage on the chemical composition of oats was determined under conditions of constant temperature, humidity and light. The changes in composition as a function of age were found to be small for K, Na, Ga and Mg but considerable in the case of N and P. In addition, a study was made of early diagnosis of mineral deficiencies by means of chemical analysis, oats being used as the test crop. The data were obtained from 18- and 25-day-old plants growing in sand cultures from which varying amounts of N, P, K or Mg were omitted. It was concluded that early diagnosis is possible provided that the fluctuation in chemical composition of normal plants is known. The rapid changes in chemical composition of crops in the field are most probably due to fluctuating concentrations of ions in the soil solution and not to small differences in stage of development. F. s.-R.B. (Abstract retrieved from CAB Abstracts by CABI’s permission)


2020 ◽  
Vol 51 (Special) ◽  
Author(s):  
Gh. A. Mam-Rasul

Sorption is one of the most chemical important processes, which determine nutrients availability in soil. Sorption isotherms provide sufficient information about soils sorption’s capacity, and it’s data can be used to determine thermodynamic sorption parameters. The aim of this studyis to evaluate the sorption of potassium onto some soils. An experiment was conducted with four calcareous soils of the Sulaimani province Kurdistan Region of Iraq by using the batch methods. 5g soil samples were equilibrated at 298±1 Kelvin with 50 ml of 0.01M CaCl2 containing 0 to 250 mg L-1 K as KCl. Suspensions were centrifuged, filtered, and concentration of K+ in the clear extract solution was determined. Amount of K+ sorbed by the soil was calculated from the difference between the initial and final concentration of K+ in the equilibrium solution. Sorption of K+ was evaluated using adsorption isotherms. The results showed that K+ sorption was described by linear, Langmuir, Freundlich, and Temkin equations. Langmuir equation gave a better fit of equilibrium K adsorption when it has a higher R2 and lowers SE.  The data indicated that the maximum monolayer coverage capacity (b) from the Langmuir isotherm model ranged between (-113.63 to 2500) mg kg-1. The negative values of (b) for studied locations soils indicated to potassium release instead of adsorption. The Langmuir isotherm constant (KL) ranged from (-0.01 to 0.01) L mg-1. Maximum buffering capacity (MBC) is a capacity factor, which measures the ability of the soil to replenish K ion to soil solution that the ability of a soil to supply K to the soil solution. The value of MBC of the studied soils ranged from 0.453 to 23.75 mg kg-1.The sorption processes for the forth locations are favorable and spontaneous because the value of RL was an equal one.


HortScience ◽  
1994 ◽  
Vol 29 (5) ◽  
pp. 576b-576
Author(s):  
Eovaldo Hernández

Most of the studies on the effect of humic acids on micronutrient uptake by plants has been carried out in nutrient solutions. Commercial companies have tried, without adequate experimental support, to extend the conclusions of these studies to the production of vegetables in agricultural soils. The effect of humic acids on micronutrient uptake by plants has been attributed' to (a) the improved supply of micronutrients to the soil solution caused by a higher rate of release from soil minerals (probably via chelate formation by humic acids) and (b) the improved uptake of micronutrients as consequence of the larger root system promoted by hormonal compounds in the humic acids. In soils with limiting concentration of micronutrients (such as some calcareous soils) and low content of organic matter, chelation of micronutrients by added commercial humic acids might increase their availability to plants. However, in agricultural soils with and adequate content of organic matter, no significant effect of commercial humic acids on micronutrient uptake by plants can be detected.


Radiocarbon ◽  
2017 ◽  
Vol 59 (1) ◽  
pp. 141-150 ◽  
Author(s):  
Kazem Zamanian ◽  
Konstantin Pustovoytov ◽  
Yakov Kuzyakov

AbstractFruit carbonate of Buglossoides arvensis (syn. Lithospermum arvense) is a valuable dating and paleoenvironmental proxy for late Quaternary deposits and cultural layers because CaCO3 in fruit is assumed to be accumulated from photosynthetic carbon (C). However, considering the uptake of HCO3– by roots from soil solution, the estimated age could be too old depending on the source of HCO3– allocated in fruit carbonate. Until now, no studies have assessed the contributions of photosynthetic and soil C to the fruit carbonate. To evaluate this, the allocation of photo-assimilated carbon and root uptake of HCO3– was examined by radiocarbon (14C) labeling and tracing. B. arvensis was grown in carbonate-free and carbonate-containing soils (sand and loess, respectively), where 14C was provided as (1) 14CO2 in the atmosphere (5 times shoot pulse labeling), or (2) Na214CO3 in soil solution (root-labeling; 5 times by injecting labeled solution into the soil) during one month of fruit development. Distinctly different patterns of 14C distribution in plant organs after root- and shoot labeling showed the ability of B. arvensis to take up HCO3– from soil solution. The highest 14C activity from root labeling was recovered in roots, followed by shoots, fruit organics, and fruit carbonate. In contrast, 14C activity after shoot labeling was the highest in shoots, followed by fruit organics, roots and fruit carbonate. Total photo-assimilated C incorporated via shoot labeling in loess-grown plants was 1.51 mg lower than in sand, reflecting the presence of dissolved carbonate (i.e. CaCO3) in loess. Loess carbonate dissolution and root-respired CO2 in soil solution are both sources of HCO3– for root uptake. Considering this dilution effect by carbonates, the total incorporated HCO3– comprised 0.15% of C in fruit carbonate after 10 hr of shoot labeling. However, if the incorporated HCO3– during 10 hr of shoot labeling is extrapolated for the whole month of fruit development (i.e. 420-hr photoperiod), fruit carbonate in loess-grown plants incorporated approximately 6.3% more HCO3– than in sand. Therefore, fruit carbonates from plants grown on calcareous soils may yield overestimated 14C ages around 500 yr because of a few percentage uptake of HCO3– by roots. However, the age overestimation because of HCO3– uptake becomes insignificant in fruits older than approximately 11,000 yr due to increasing uncertainties in age determination.


2016 ◽  
Vol 47 (4) ◽  
Author(s):  
Jar Allah & et al.

Laboratory experiment was carried out in order to study the adsorption of Fe as FeEDDHA  as related to some soil properties in six calcareous soils from the middle of Iraq. Langmuir, Freundlich and Temkin equations were used for describing Fe adsorption. The best equation was chosen according  to highest value of r, r2 and t and least value of Standard error of estimate.   The results showed that Freunglich equation was more efficient for describing Fe sorption  compared with other physicochemical equations used, depending on highest values of, r  (0.985),  r2 (0.970) and t ( 20.01) and lower standard error SE.e (0.186). Maximum adsorption capacity in tested soils were 415.2, 393.7, 353.7, 344.2, 318.4 and 306.0 µg Fe g-1soil while the binding strength were    0.059, 0.046, 0.059, 0.051, 0.059 and 0.064 ml Fe µg-1 for Balad, Al-Khalis, Al-Raaid, Al-Wehda, Al-Mussayib and Al-Rashidaaa. 59.2% of the applied Fe was sorbed on soil while 40.8%  remained soluble in soil solution. Freunglich adsorption constants (lnKf and 1/n) significantly correlated with Langmuir maximum adsorption (b) and binding strength (K). Also, the maximum adsorptive capacity (b) of  Langmuir models statistically related to soil properties (EC, total and active carbonate  and plant available Fe). It can be concluded from  this study that Freunglich and Langmuir equations were more suitable for describing Fe adsorption in all tested soils. Tested soils sorbed Fe according to the following arrangement: Balad > Al-Khalis > Al-Raaid > Al-Wehda > Al-Mussayib > Al-Rashidaa.


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