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Water analysis examples

Hitchon B. (1996) Rapid evaluation of the hydrochemistry of a sedimentary basin using only standard formation water analysis example from the Canadian portion of the Williston Basin. Appl. Geochem. 11, 789-795. [Pg.2787]

Environmental Analysis One of the most important environmental applications of gas chromatography is for the analysis of numerous organic pollutants in air, water, and wastewater. The analysis of volatile organics in drinking water, for example, is accomplished by a purge and trap, followed by their separation on a capillary column with a nonpolar stationary phase. A flame ionization, electron capture, or... [Pg.571]

Quantitative analytical methods using FIA have been developed for cationic, anionic, and molecular pollutants in wastewater, fresh waters, groundwaters, and marine waters, several examples of which were described in the previous section. Table 13.2 provides a partial listing of other analytes that have been determined using FIA, many of which are modifications of conventional standard spectropho-tometric and potentiometric methods. An additional advantage of FIA for environmental analysis is its ability to provide for the continuous, in situ monitoring of pollutants in the field. ... [Pg.655]

Consultants are equipped to monitor the quality of freshwater, estuarine and marine environments and can make field measurements of a variety of water-quality parameters in response to pollution incidents. For example, reasons for the mortality of marine shellfish and farmed freshwater fish have been determined using portable water-analysis equipment. Various items of field equipment are, of course, also employed in baseline studies and monitoring, respectively, before and after the introduction of new effluent-disposal schemes. [Pg.40]

This section covers some examples and notes on common but unrelated problems, all of which rely in part on the effective observation of boiler plant operating conditions and the interpretation of daily water analysis log sheets. [Pg.657]

The emphasis that the FQPA placed on the assessment of pesticide residues in drinking water, for example, led to the collection and analysis of data on the effects of drinking water treatment processes on pesticide residues. These data were presented to the FIFRA Science Advisory Board to highlight the variability in the effects of treatment on different kinds of pesticides and the products formed and the variability of treatment processes employed at different locations and at different collection time intervals at an individual location. These complexities led to the current proposal... [Pg.614]

The usefulness of NMR in such analysis is because the proton spin-relaxation time constants are different for different components, such as water, liquid fat and solid fat. For example, the signal from solid fat is found to decay rapidly while the liquid signals decay much slower. This phenomenon is the basis for an NMR technique to determine the solid fat content [20], However, as the relaxation time constant of water, for example, could depend on its local environment, such as protein concentration, it may overlap with that of oil and other components. As a result, it could be difficult to formulate a robust and universal relaxation analysis. It... [Pg.163]

The solubility of water in a water-immiscible solvent at water activity 1 can be determined by equilibrating the solvent with pure water, followed by water analysis, for example, by Karl Fischer titration. At water activities lower than 1, lower amounts of water dissolve in the solvents, as shown in Figure 1.3. It should be noted that the solubility of water in the solvent changes when solvent composition is changed, for example, by dissolving substrates (Figure 1.3). In a hydrophobic solvent the increase in solubility of water can be substantial when substrates are dissolved in it. [Pg.7]

In addition, there exist a multitude of different applications in water analysis by ICP-MS for environmental control. For example, Lawrence et cdP determined rare earth element concentrations in natural waters (these are river, lake, sea or groundwater) by quadrupole ICP-MS using external calibration and employed river water reference material SLRS-4 to validate the analytical data. The speciation of yttrium and lanthanides in water samples by SEC-ICP-MS was studied by Haraguchi et a/.18 whereby the detection of La, Ce and Pr corresponded to the occurrence of large organic molecules. [Pg.301]

Solid-state ion sensors with conducting polymers as sensing membranes have also proved useful in some applications. Of particular importance are the pH sensors based on polyaniline that can be also applied in non-aqueous solutions. Polypyrrole-based sensors for nitrate also show great promise for water analysis. However, in addition to these two excellent examples, a large number of functionalized conducting polymers have been synthesized already, and these materials may offer unique possibilities for fabrication of durable, miniaturized ion sensors. [Pg.81]

I venture to say that the majority of practical chemometrics applications in analytical chemistry are in the area of instrument specialization. The need to improve specificity of an analyzer depends on both the analytical technology and the application. For example, chemometrics is often applied to near-infrared (NIR) spectroscopy, due to the fact that the information in NIR spectra is generally non-specific for most applications. Chemometrics may not be critical for most ICP atomic emission or mass spectrometry applications because these techniques provide sufficient selectivity for most applications. On the other hand, there are some NIR applications that do not require chemometrics (e.g. many water analysis applications), and some ICP and mass spectrometry applications are likely where chemometrics is needed to provide sufficient selectivity. [Pg.227]

Accurate electrolytic conductivity measurements are required, for example, in water purity assessment which is needed by the pharmaceutical and semiconductor industries and in power plants, for the evaluation of the water quality under regulatory requirements and for water analysis in environmental monitoring. [Pg.145]

The Feed analysis screen is reached via the menu under "Tools— Input—Water Analysis," or by the "HzO" button at the top of the main screen. Up to three feed analyses can be entered. Concentration can be entered as ppm ion, ppm as calcium carbonate, or as milli-equivalence per liter. Standard species, such as calcium and sodium, are entered. There is also space for four designer-defined species of interest. Examples of designer-defined species include total organic carbon, boron, and the like. Note that the program will not automatically calculate permeate and concentrate concentrations for these designer-defined species. [Pg.231]

Furthermore, water analysis must estabhsh the process-affecting constituents of the water matrix, such as for example,... [Pg.255]

Using traditional methods of whole-water analysis, concentrations of these HCs are usually underestimated. Indeed, by these methods HCs may not even be detected, although they may occur on sediment at concentrations likely to have toxic effects on biota. The conventional approach for determining the concentration of HCs on suspended sediment is to analyze a whole-water sample and a filtered water sample and to assume that the difference between the two represents the fraction sorbed to suspended sediment. The major problem with this approach is that the amount of suspended sediment and associated contaminant in the whole-water sample may not be sufficient to produce a detection by whole-water analysis methods. This is particularly true if the suspended sediment concentration in the sample is small, as is generally the case for springs relative to surface water. For example, if a sample contains 50 mg/L of suspended sediment, and the sediment contains 300 pg/kg of polychlorinated biphenyls (PCBs) (a concentration likely to adversely affect biota health (Environment Canada, 1998)), the concentration of PCBs in the whole-water sample will be 0.015 pg/L. This concentration is well below most laboratory method detection limits—for example, the USGS National... [Pg.39]


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