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The Buffer Concept

A buffered system is one that resists changes to its intensive variables. In other words, changing the composition of a buffered system will result in less change to certain properties than would occur in an unbuffered system. In chemistry, p buffers are common. In geology, the buffer concept has been extended to many other intensive variables such as O2 fugacity (Eugster, 1957), and HC1° and HF° activities (Zhu and Sverjensky, 1991). [Pg.211]

The most familiar buffers, which we first learned about in high school chemistry, are mixtures of a weak acid and its salts. These are compositions that, when present in a solution, will use up or supply H+, so that the pH is held close to some desired value when composition is changed, as during a titration. [Pg.211]

For a solution of acetic acid and sodium acetate, for example, the following equilibrium holds  [Pg.211]

The CO2 - HCO - CO2- equilibrium is just such a homogeneous buffer in natural waters. However, the buffer capacity is much smaller than that provided by heterogeneous buffers (Stumm and Morgan, 1996). [Pg.211]

The most common heterogeneous buffer in the acidic and near neutral pH range in natural environments is calcite, the dissolution and precipitation of which can be represented by [Pg.211]


The buffer concept helps us understand what reactions control the pH of natural waters including soil waters (cf. Van Breemen and Wielemaker 1974) and wastewaters. [Pg.180]

By February 1912, however, having become fully convinced of the primacy of carbonic acid and water in the environment and the importance of the buffer concept, he set about writing The Fitness of the Environment. He claimed that he made no outline of the book (or of later ones, for that matter, including the treatise on Blood) and spent less than sixty days (and probably closer to fifty) writing the volume (p. 186). [Pg.7]

This study has been included partly because it illustrates the usefulness of the buffering concept, which is the basis of the method. The actual value of the interaction coefficients in garnets are still a subject of some debate, as discussed by Newton and Haselton (1981). [Pg.405]

An alternative system proved to be both simpler and more user friendly (Unger et al., 2004 Machtejevas et al., 2006). Thus far we have used this configuration to analyze human plasma, sputum, urine, cerebrospinal fluid, and rat plasma. For each particular analysis we set up an analytical system based on a simple but specific strategy (Figure 9.5). The analysis concept is based on an online sample preparation and a two-dimensional LC system preseparating the majority of the matrix components from the analytes that are retained on a RAM-SCX column followed by a solvent switch and transfer of the trapped peptides. The SCX elution used five salt steps created by mixing 20 mM phosphate buffer (pH 2.5) (eluent Al) and 20 mM phosphate buffer with 1.5 M sodium chloride (eluent Bl) in the following proportions 85/15 70/30 65/45 45/55 0/100 with at the constant 0.1 mL/min flow rate. Desorption of the... [Pg.214]

However, toward the end of the 19th century, there were still some things about soils and chemistry that inhibited an understanding of much of soil chemistry. The concepts of pH and ions had not yet been developed. Although clay was known and had been known for centuries, the varieties of clays in soil were not known and thus their effect on soil chemistry was unknown. The basic concepts of ion exchange and buffering were also not yet understood either in chemistry or in soils. [Pg.25]

Our goal in this chapter is to help you continue learning about acid-base equilibrium systems and, in particular, buffers and titrations. If you are a little unsure about equilibria and especially weak acid-base equilibria, review Chapters 14 and 15. You will also learn to apply the basic concepts of equilibria to solubility and complex ions. Two things to remember (1) The basic concepts of equilibria apply to all the various types of equilibria, and (2) Practice, Practice, Practice. [Pg.236]

The first summation Incorporates a block data set for observed monomeric standards the second is a null buffer the third are polymeric standards. Testing through the addition of monomers to polymer standards verified that the decomposition concept is again valid. Accuracy within the chromatogram is the error-determining step. Table I presents analysis of material after blending known quantities. [Pg.121]

The isolation and safety functions of HLNW deep geological repositories are based upon the multibarrier concept, where a number of containment and isolation barriers are put in place. A schematic view of the multibarrier HLNW concept is given in Fig. 1. The main barriers of the system are the waste matrix itself a metallic container (either corrosion resistant like Cu or Ti, or based upon stainless steel) a buffer material (normally bentonite) and finally the host rock itself (essentially granite or clay, although salt domes are also being considered). [Pg.516]

With the concept of Diphoterine , even the restoration of glutathione contents in the burnt cornea can be achieved without any action of the regenerating tissues. This is a major value. Dimercaprol has similar effects and might be an opportune alternative, but this drug does not act on alkali and acids as well as the buffers and amphoteric substances do. [Pg.87]

Obtain a dimensionless relation for the velocity profile in the neighbourhood of a surface for the turbulent flow of a liquid, using Prandtl s concept of a Mixing Length (Universal Velocity Profile). Neglect the existence of the buffer layer and assume that, outside the laminar sub-layer, eddy transport mechanisms dominate. Assume that in the turbulent fluid the mixing length Xe is equal to 0.4 times the distance y from the surface and that the dimensionless velocity u1 is equal to 5.5 when the dimensionless distance y+ is unity. [Pg.310]

It is often necessary to control the pH of a solution in circumstances where hydrogen ions are being generated or absorbed. The buffer solution concept developed above is a versatile and widely used method of pH control. A buffer may be prepared to meet a particular pH requirement by the use of standard pKt values in conjunction with equation (3.21). This equation gives a good approximation provided that the solution contains at least 0.1 mol dm-3 of the buffer and that the required pH lies close to.the value of pKt. For example, if a solution needs to be buffered to pH = 9, the anjmonium ion (pAfa -> 9.62) can be used. Substitution in equation (3.20) enables the necessary solution composition to be calculated... [Pg.47]

Aqueous solutions are well buffered at either extreme of the pH scale. If in an alkalimetric or acidimetric titration curve the pH at the equivalence point falls into a pH range where the buffer intensity caused by [H ] or [OH ] exceeds that of the other protolytes, obliteration of a pH jump at the equivalence point results (see Figure 3.11). The concept of pH buffers can be extended to ions other than H" ". Metal-ion buffers will be discussed in Chapter 6. [Pg.135]

The concept of buffer intensity considered above may be extended and defined in a generalized way for the incremental addition of a constituent to a closed system at equilibrium. Thus, in addition to the buffer intensity with respect to strong acids or bases, buffer intensities with respect to weak acids... [Pg.136]

On the basis of these three cross coupling reactions, it is probably fair to say that using the OSSOS concept is highly compatible with palladium catalysis but probably not limited to it. For example, a lipase can be used for the kinetic resolution of a racemic ibuprofen ester supported on an imidazolium salt. In a DMSO/phosphate buffer mixture and in the presence of the lipase isolated from Candida antartica, the, V-(+(-supported ibuprofen ester is hydrolyzed selectively (87% ee) in 87% yield. Noticeably, during workup, the support can easily be recovered and reused for another cycle while the other enantiomer can be obtained by hydrolysis using K2CQ3 [137] (Fig. 48). [Pg.119]

The concept of pH buffer capacity as a measure of resistance to pH change can be applied to our thinking about the buffering of environmental systems with respect to their concentrations of other substances, including electrons (as defined by redox potential, cf. Nightingale 1958) or contaminant trace metals (cf. Pankow 1991). [Pg.180]


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