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Alkaline front

Most investigators agree on the necessity of avoiding the development of an alkaline front from the cathode compartment into the soil since most heavy metals precipitate/adsorb to the soil in the alkaline environment, and the result is that the remediation process ceases, as shown in many of the early works on EK soil remediation (Kim and Kim, 2001). Most commonly, pH control maintains acidic conditions in the cathode compartment, and thus efficiently prevents the alkaline front from developing into the soil (Hicks and Tondorf, 1994 Wieczorek et al, 2005). Implementation of ion exchange membranes as mentioned above is another way to prevent the alkaline front (Hansen et ai, 1999). In laboratory experiments, the soil is commonly homogenized and the water is saturated. In full-scale experiments, the situation is different Here the electrode compartments are placed directly into the inhomogeneous soil, whose humidity is decided by the natural precipitation, as these systems are open and most often in situ. This could be one major reason why the scale up from laboratory cell experiments to full-scale remediation is so difficult (Hansen et al, 1997 Ottosen et al, 1997). [Pg.99]

For some combinations of heavy metals, it is also necessary to use enhancement solutions to ensure the simultaneous removal of all pollutants (Ottosen et ai, 2003). Especially, the presence of As in the soil necessitate alternative solutions to the acidic front since As generally has low mobility under acidic conditions, whereas As is more mobile under alkaline conditions, where most heavy metals are not mobile (Le Hecho, TelUer, and Astruc, 1998 Ottosen et aL, 2000). Le Hecho, Tellier, and Astruc (1998) conducted laboratory experiments with spiked soils, where the pollutants were As and Cr. Successful remediation was obtained in the developing alkaline front combined with the injection of sodium hypochlorite. As was mobile in the alkaline environment, and Cr(III) was oxidized to Cr(VI) by hypochlorite and mobilized in the alkaline environment. In loamy sand polluted with Cu and As from wood preservation. As and Cu were mobile simultaneously after the addition of NH3 to the soil (Ottosen et a/., 2000). As was mobile due to the alkaline environment and Cu formed charged tetra-ammine complexes. For the simultaneous mobilization and electrochemical removal of Cu, Cr, and As, ammonium citrate has shown to be successful (Ottosen et al, 2003). [Pg.114]

The simplest way to apply EK soil remediation to a heavy metal-polluted soil is to utilize the acidic form that develops from the anode side to obtain desorption (and prevent the alkaline front from the cathode). This system works well in general for Cd, Cu, and Zn in most soils. [Pg.119]

Virkutyte J, SUlanpaa M. (2007). The hindering of experimental strategies on advancement of alkaline front and electroosmotic flow during electrokinetic lake sediment treatment. Journal of Hazardous Materials 143 673-681. [Pg.126]

Chromate Red mud, which contains about 35% hematite, has been used effectively in a PEREBAR coupled with electrokinetics (De Gioannis et al, 2007). The red mud is located near the anode so that the acid produced at the anode is partially neutralized, allowing the alkaline front to move through the soil, under... [Pg.353]

Most often, inert electrodes are chosen, and the major electrode reactions are electrolyses, resulting in acidification around the anode and an alkaline environment around the cathode. Subsequently, an acidic front develops in the soil from the anode towards the cathode as the remediation progresses. The analogous alkaline front from the cathode is, however, hindered in developing in the opposite direction by maintaining the catholyte as acidic. This means that over time the whole soil volume between the electrodes becomes acidified, and in the acidic conditions, most heavy metals are desorbed and precipitates dissolved. The hereby mobilized heavy metals are transported into the processing solutions at the electrode by electromigration. [Pg.743]

The visual limit of detection was between 30 and 50 ng per chromatogram zone for nickel and copper, a factor of ten worse for the alkaline earths. There was sometimes an impurity front in the same hRf range as beryllium. [Pg.146]

Alkaline soil conditions exist in most semi-arid to arid conditions. Oxidizing sulfides should produce a change in pH in the surface soil as confirmed by Hamilton et al. (2004), and especially in the soil microlayer where an upward moving front of H" accumulates, as shown nearly 40 years ago. If this soil micro-layer is sampled... [Pg.92]

Figure 1.1 Principal features of the periodic table. The International Union of Pure and Applied Chemistry (IUPAC) now recommends Arabic group numbers 1-18 in place of the traditional Roman I—VIII (A and B). Group names include alkali metals (1), alkaline earth metals (2), coinage metals (11), chalcogens (16), and halogens (17). The main groups are often called the s,p block, the transition metals the d, block elements, and the lanthanides and actinides the / block elements, reflecting the electronic shell being filled. (See inside front cover for detailed structure of the periodic table.)... Figure 1.1 Principal features of the periodic table. The International Union of Pure and Applied Chemistry (IUPAC) now recommends Arabic group numbers 1-18 in place of the traditional Roman I—VIII (A and B). Group names include alkali metals (1), alkaline earth metals (2), coinage metals (11), chalcogens (16), and halogens (17). The main groups are often called the s,p block, the transition metals the d, block elements, and the lanthanides and actinides the / block elements, reflecting the electronic shell being filled. (See inside front cover for detailed structure of the periodic table.)...
Anions, including arsenic oxyanions and OH-, migrate toward the anode. The negatively charged cathode attracts metal cations and creates reducing conditions and an alkaline (perhaps pH > 12) front in the surrounding waters (Acar and Alshawabkeh, 1993, 2638) ... [Pg.408]

A less common circumstance leading to hypercalcemia is development of a form of osteomalacia characterized by a profound decrease in bone cell activity and loss of the calcium buffering action of bone. In the absence of kidney function, any calcium absorbed from the intestine accumulates in the blood. Therefore, such patients are very sensitive to the hypercalcemic action of l,25(OH)2D. These individuals generally have a high serum calcium but nearly normal alkaline phosphatase and PTH levels. The bone in such patients generally has a high aluminum content, especially in the mineralization front, which may block normal bone mineralization. These patients do not respond favorably to parathyroidectomy. Deferoxamine, an agent used to chelate iron (see Chapter 58 ... [Pg.1027]

Enzymes can be liberated from enteric-coated formulations by the neutral to slightly alkaline pH caused by secretions front die pancreas, the gall bladder, and the intestinal mucosa. They have a hydrogen carbonate concentration of about SS mM, which causes an increase in pH. Bile salts decrease the interfadal tension, promoting the liberation of drugs from solid dosage forms. [Pg.3]

In general, alkali metal salts damp muzzle flash better than alkaline earth salts. It is also fairly certain that the flash-damping effect in the alkali metal group increases from lithium to cesium. In the First World War, bags filled with sodium chloride placed in front of the propellant charge, was used as a muzzle flash damper. [Pg.279]

Test the contents of both jars with red and blue litmus paper to see which solution is acid and which solution is alkaline. Place the jar of acid directly in front of you. Place the alkaline solution to the right and slightly behind the acid (unless you are left-handed). Now, with the dropper near the calcium hydroxide, add 3 drops of it to the acetic acid, stir with the spoon near the acetic acid, and test the new solution with blue litmus paper. Repeat this procedure over and over, counting the drops carefully, and noting the amount of change in... [Pg.72]

The test solution should not contain more than 5 per cent (v/v) concentrated hydrochloric acid and must have a pH < 2. It is spotted on a paper strip and allowed to evaporate for 10-15 minutes. Diffusion of the solvent takes place in an atmosphere saturated with respect to the vapour of a saturated solution of methyl acetate in water, and the temperature is maintained constant at 22°. The solvent moves sufficiently far in 20-30 minutes to effect a complete separation. After evaporation of the solvent, the strip is made alkaline by exposure to ammonia vapour and then sprayed with a 1 per cent solution of diphenyl-carbazide in alcohol. Mercury is indicated by a narrow blue band in the dry solvent front. [Pg.504]


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See also in sourсe #XX -- [ Pg.99 ]




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