Relationship between ionic strength and electrical conductivity for soil solutions

Relationship between ionic strength and electrical conductivity for soil solutions

the high ionic strength of the soil solution. The measurement of ionic strength of a soil can be determined from the electrical conductivity (EC) of a at any one time and have obtained good relationships between soil solution pH (prt,.,) and. Jul 1, Studies of plant nutrient requirements in solution culture have often used nutrient concentrations many-fold higher than levels found in fertile soil. conditions of low ionic strength and electrical conductivity (EC −1). .. Solution temperatures varied between 19 °C and 23 °C during the light. The ionic strength of the soil solution (p) extracted from the soils of equation showed a strong relationship between change in negative charge with ionic .. where EC= the soil solution electrical conductivity at 25°C expressed as mS cm-I.

Seeds of Triticum aestivum L. Katepwa were surface-sterilized in a 1. Seedlings were thinned after 3 d to plants per aquarium.

Nutrient additions for each day At were calculated using equation 3. Calculated nutrient additions for the pretreatment period were reduced by half in the experiments reported later in Figs 6—10as seed reserves were providing seedlings with sufficient nutrients to accelerate the RGR beyond desired levels. The dry weight of plants for the final day of the pretreatment period was used to estimate W0 for the calculation of nutrient additions for the experimental period.

After 9 d, spent seeds were removed from all plants and eight uniform seedlings were transferred to each of 60 polyethylene containers filled with 10 l of aerated background solution.

Solutions were adjusted to pH 4. Seedlings were mounted on opaque Plexiglas covers, which were placed over the containers to limit algal growth. Distilled water was added periodically to the nutrient solutions to compensate for water loss by evaporation and transpiration. Containers were suspended in a common water bath to limit temperature fluctuations and to maintain a constant temperature across all experimental solutions. Measurements were taken prior to planting, three times per week just before nutrient additionsand immediately after harvest.

Experiments were conducted in two controlled-environment growth chambers, with 16 h light and 8 h darkness. Electrical conductivity and pH were determined in a soil: Soil textural fractions were quantified according to the Bouyoucos method Claessen, Description of the solution sampler The Suolo Acqua sampler Figure 1aproposed in this study as an alternative sampler to HM, is constituted by an internal inert filter membrane previously decontaminated in successive washings with hydrochloric acid and deionized water, covered by porous hard plastic whose internal body is connected to a flexible silicone tube.

The operating principle of Suolo Acqua consists of the application of vacuum suction, which generates a potential gradient in the soil around the capsule, inducing soil solution to flux into the porous membrane. The collected soil solution is then stored in a 20 mL previously conditioned vacuum tube Figure 1b.

The hydrophilic membrane sampler is composed of a chemically inert porous hydrophilic polymer blend of polyethersulfone and polyvinylpyrrolidone of 0. Inside the PVC pipe, there is a stainless steel wire used to reinforce the sampler structure. Soil solution sampling Solution samplers were installed in a 0. The sampler was installed so as to keep it in the center of each pot. Solution samplers were carefully inserted in soils, and fine soil with aggregates of approximately 1 mm were lightly compressed around the sampler capsules to prevent air bubbles and discontinuity of the soil-water-sampler system.

After sampler installation, deionized water was added to reach soil water content near field capacity.

CONDUCTIVITY :To determine the conductivity of soil sample - EXPERIMENT - CHEMISTRY- BY CBR

Soil moisture was kept at this level for a period of 12 h, aiming at equilibrium between the soil and its liquid phase. The soil solution was sampled at 0, 2, 4, and 14 days after beginning soil incubation. Soil solution samples were collected with a 20 mL tube previously conditioned to kPa vacuum pressure. This standardized vacuum level was generated with the aid of a vacuum pump, allowing the collection of about 15 mL of soil solution.

A hypodermic needle was placed at the end of the solution header pipe of each sampler, and this needle was inserted in the rubber sealing cap of the plastic tube used to store the soil solution. After 10 h, the solution collected in the vacuum-conditioned tubes was filtered through membranes of 0. The chromatographic standard curve was prepared using certified solutions from Dionex, whose concentrations ranged from 0.

Certified samples from Elementar of potassium acid phthalate and sodium carbonate were used as organic and inorganic C standards, respectively, to calibrate the automated TOC analyzer. Solution EC and pH were measured in unfiltered solution samples within a 24 h collection. A multiple parameter regression analysis was also performed to evaluate the degree of association of EC with solution pH, ion concentrations, and C contents. There was no significant effect of the interaction between solution samplers and sampling time on the chemical properties analyzed in the three soils incubated.

Over the sampling period, the anion concentrations vary, and the magnitude of these variations is soil-dependent. Differences in the chemical composition of the solution over the sampling period are related to biochemical and chemical processes that occur at the same time as the nutrient transfer rates and reactions between the solid and liquid phase increase.

Due to precipitation with cations or adsorption in oxides and other minerals of low chemical activity found in the soil clay fraction, sulfate concentration may also diminish in the soil solution.

Over time, soil organic mineralization and nitrification rates may increase, which may explain, at least in part, the increase in solution nitrate concentrations. Thus, variations in solution chemical composition over the sampling period signal the fact that soil solution sampling must be performed over time to correctly evaluate the dynamics of soil chemical composition.

Content of anions in solution also changed in the CXbd samples, whereas concentration of anions in the RQ solution only changed slightly over the sampling period.

As already mentioned, the magnitude of the diverse processes and reactions between the liquid and solid phase, which are specific to each soil, affect the levels of anions dissolved in the liquid phase. Based on this assumption, the role that soil OM decomposition, microbial activity, and equilibrium reactions between the liquid and solid phase have over the soluble anion contents must be emphasized Gloaguen et al.

In tropical soils, adsorption of phosphate ions is high, due to the low amount of negative charges and the presence of Fe and Al oxides in the clay fraction of weathered soils, which may explain the reduced levels of P found in the Brazilian soil solution investigated. The reduced amounts of P determined in the soil solutions of the Brazilian soils studied must be highlighted because P scarcity is a serious factor limiting high crop yield and enhanced uptake of other nutrients when P-fertilization is not correctly performed in Brazilian crop fields.

Although differences in the chemistry of the solution were hardly observed for the two samplers tested, soils presented different amounts of analytes in their solutions. These higher cation concentrations observed for the LHd and CXbd may be due to the higher clay and OM verified in these soils. In more buffered solid phase soils, cations stored in organic and inorganic colloids can gradually be released to the solution, which may increase cation availability in the soil liquid phase Ronquim, Similar behavior for concentrations of these three cations in solution matrices was also observed by Miranda et al.

Soil solutions were collected by the Suolo Acqua and hydrophilic membrane HM samplers. Greater recovery of C-soluble fractions by Suolo Acqua in relation to HM Figure 4 may be explained by the presumed selectiveness of HM for organic molecules of high molecular weight. The HM pore diameter 0. The use of Suolo Acqua does not result in retention or selectiveness in extraction of organic substances present in the solution because the sampler does not have a defined pore diameter.

It should be noted that after extraction, the Suolo Acqua solutions were filtered again through a cellulose membrane with a 0. Taking into account that the HM pore is designed to retain some microorganisms, it should be investigated if this selectiveness is also followed by some restriction to free or complexed organic compounds found in the soil solution.

Variables were measured in solutions extracted in four sampling times by the Suolo Acqua and hydrophilic membrane HM samplers. The SIC concentrations in the LHd and CXbd solutions changed only slightly over time, although significant increases in solution analytes were verified in the last sampling time. Such results are not uncommon, since the soluble C content in the soil depends on its OM content Pinheiro et al.

Thus, high contents of C in the LHd 6.

The soluble C concentrations are directly related to the amounts of C stored in the soil as a whole Ciotta et al. The solution pH changed over the sampling period, ranging from 5. Over the sampling period, the lowest pH value in the LHd solutions was verified at the beginning of soil incubation. In the RQ samples, the solution pH ranged from 5. In the CXbd samples, the solution pH ranged from 5.

Soil pH is one of the most important properties that affects the composition of the solution since it controls solubility and concentration, determines the intensity of the reactions in the soil, affects the ionic form of the nutrients in the soil solution, and modulates the intensity of sorption processes. Solution EC is directly associated with salt and ion concentrations found in soils.

Changes in solution EC are due to variations in the availability of ions in the soil solution, as verified by Sahrawat and Narteh The EC fluctuations are inversely correlated to solution pH over the sampling period in the three soils. Such results may be explained by the lower concentrations of anions, cations, and C in the solutions of the RQ, the soil with low clay and organic matter contents.

The increased capacity of soils rich in clay and organic matter in retaining nutrients may explain higher concentrations of salts and ions in the solution and, consequently, the higher solution EC values verified in the LHd and CXbd samples compared to the RQ samples.

Variations in the chemistry of solutions are dependent on the soil investigated and are dependent on the sampling time.

Relationships between ionic strength and electrical conductivity of water and aqueous soil extracts

Overall, it is necessary to check if the levels of analytes in the solution verified in this study are below or above the levels considered critical for adequate plant growth or environmental analysis. Critical nutrient levels or ranges for the purpose of suitable plant growth in formulated substrates are described in Abad et al.

Critical levels of nutrients in hydroponic solutions are also a reference for evaluating the levels of nutrients in the soil solution. A comprehensive review of nutrient levels and their critical levels in the soil solution for optimum plant growth are shown in Smethurst By using the aforementioned critical nutrient levels, it is possible to assess the limitations or excesses of nutrients in the soil solutions investigated.

N-ammonium levels are too low because when they are totaled with the N-nitrate levels, they are lower than the range considered adequate for N in hydroponic solutions. The solution S contents are less than 30 mg L-1; therefore, levels of S available in the solutions are also a factor limiting plant growth. The contents of Br and F are very low; thus, no toxicity problems for plant growth are expected for these two chemical elements.

Solution P levels are extremely limiting to plants in all the soil solutions investigated since the levels are below the low quantification limit of this nutrient by the ion chromatography technique used. The pH values were within the range considered appropriate in the initial solution sampling times, but they reach values in the alkaline range in subsequent solution sampling.

Thus, multiple nutritional deficiencies are expected in these alkaline soils. As a whole, solution EC values are considered low, since they are lower than 0. This result demonstrates that the EC in the soil solution increases as the pH decreases and as the concentrations of anions, cations, and total C in the solution increase, making the EC in the solution a complex and dynamic property which reflects the effects of several properties of the solution acting together.