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Water testing limitations

Specifications for gas turbine fuels prescribe test limits that must be met by the refiner who manufactures fuel however, it is customary for fuel users to define quality control limits for fuel at the point of delivery or of custody transfer. These limits must be met by third parties who distribute and handle fuels on or near the airport. Tests on receipt at airport depots include appearance, distfllation, flash point (or vapor pressure), density, freezing point, smoke point, corrosion, existing gum, water reaction, and water separation. Tests on delivery to the aircraft include appearance, particulates, membrane color, free water, and electrical conductivity. [Pg.411]

Gas-absorption rates furnish another test of the magnitude of effect (i). If the gas is pure (e.g., CO2 at a partial pressure of 1 atm.), and is absorbing into stirred liquid, then the momentum-transfer term ijiRci is always negligible thus an interfacial film can reduce 2 only through effect (i) above. The results of Davies and Kilner (1, M) show that for the absorption of CO2 into water, the limiting value of factor (i), by which the film reduces /c2, is 1.9 (i.e., 1.96/1.04). This may be compared with the figure of 2.2 quoted above for the ethylacetate-water system. [Pg.30]

Water systems. The water systems at ABC Pharmaceutical Industries are monitored per manufacturing site SOP for Microbiological Monitoring of Water. The levels of water tested are city water, purified water (deionized water), and water for injection (WFI). Manufacturing site SOP describes the procedures for obtaining samples, sampling frequencies, test procedures, and acceptance criteria (alert and action limits). [Pg.527]

Solubility characteristics in suitable solvents, including color and clarity evaluation pH value if API is soluble in water Microbial limits testing... [Pg.413]

Valve Trays The amount of work reported thus far on valve tray regime transition is small and entirely based on air-water tests. Correlations proposed to date require the knowledge of liquid holdup at transition, which is generally not available, and are therefore of limited application for commercial columns. [Pg.48]

Water system qualification and requalification data, along with periodic water testing, will reveal any critical excursions and alert QA to the need to withhold product from the market. Establishing alert and action limits for this crucial raw material, particularly since it is used pervasively, can go a long way in supporting QA in recall prevention. [Pg.538]

Water and Loss on Drying In general, for compounds containing water of crystallization or adsorbed water, a limit test, to be determined by the Karl Fischer Titrimetric Method, is provided under the heading Water. For compounds in which the loss on drying may not necessarily be attributable to water, a limit test, to be determined by other methods, is provided under the heading Loss on Drying. [Pg.6]

Place a drop of the test solution in a semimicro test-tube, add a drop of the reagent, a drop of dilute nitric acid (1 1), and dilute to about 2 ml. Chromates give a red colouration this is best observed with a white light behind the tube. The reagent consists of a saturated solution of chromotropic acid in water. Concentration limit 1 in 5,000. [Pg.259]

Other bioassays reported in the literature using rat (Aune and Berg 1986 Heinze 1996 Fladmark 1998) or salmon (Fladmark 1998) hepatocytes have been proposed as a monitoring tool for the peptide hepatotoxins. However, operational difficulties in water testing laboratories (e.g., preparation of cell suspensions) and limitations of sensitivity in the case of rat hepatocytes preclude then-use on a routine basis for water samples. Responses in these systems may well correlate with mammalian toxicity, thereby producing a measirre of toxicity in microcystin-LR toxicity equivalents if microcystin-LR were used for calibration. They may, therefore, be an attractive option in the futrrre with further development. [Pg.259]

Due to space limitations, all water tests that might be useful in textiles cannot be described here. The following selected tests are the ones that are most often used in textile manufacturing. These descriptions are abbreviated, and references are given in each case to more detailed explanations of the tests. [Pg.250]

There has also been concern that the temperature of the water under the oil is raised when oil spills are burned on water. Measurements conducted during tests showed that the water temperature is not raised significantly, even in shallow confined test tanks. Thermal transfer to the water is limited by the insulating oil layer and is actually the mechanism by which the combustion of thin slicks is extinguished. [Pg.156]

In the sludge material, the lead is present in the feed solution as lead sulfate. With a solubility of 0.029 g/1 in cold water (5), most of the lead is in the precipitated form but an amount far exceeding the TCLP test limits is in solution. Figure 5 shows the species of lead in solution as a function of pH (6). The diagram shows that lead is highly soluble at very low pH values as the divalent cation and at high pH values as the monovalent anion. [Pg.940]

Surface-active materials the presence of solubilizing agents alters the bioavailability of the test compounds significantly the apparent increase of the total (but not bioavailable) concentration in the water phase, possibly above the water-solubility limit for chemicals of low water solubility and high lipophilicity, may cause spuriously low BCF values (i.e. experimental artefacts). [Pg.132]

Detecting peroxides. There may be times when you need to know the peroxide content of a chemical and there are several methods that test for the presence of peroxides, including iodide methods, ferrous thiocyanate methods, titanium sulfate methods, and test strip methods. These methods each have their limitations—some will not detect the presence of all peroxide forms. These methods should not be used to test alkali metals or amides since they react violently with water. Test strips offer some advantages in that they detect a wide group of different peroxides, can be used easily, and are convenient. However, they have limited shelf life and may be beyond the budget of some. For example, potassium iodide-starch test strips are available that can detect peroxides below 100 ppm. The presence of peroxides is detected by deep dark blue (virtually black) color on the test strip from the reaction of iodine (from potassium iodide reaction with peroxide) and starch. We will not discuss these peroxide test methods in detail here, but you should know that they are available. [Pg.282]

A conductivity measurement is often used as a limit test, for example, when testing water for injection (see Sect. 27.5.2) but can also be used as part of the quality characteristics for other materials. The principle is to measure the resistance of a column of liquid in a conductivity cell. For water testing it is generally an in-process control. [Pg.721]

In this case the PVC was extracted in water for thirty minutes at 110 C using a surface area to water volume ratio of 50 cm per 10 ml. These conditions and the test limits quoted for the first three tests are those given in BS 2463 (17). Other specifications require different extraction and use slightly different test limits and normally require measurement of UV absorption in addition but the test limits shown are fairly typical requirements. [Pg.380]


See other pages where Water testing limitations is mentioned: [Pg.126]    [Pg.10]    [Pg.39]    [Pg.137]    [Pg.471]    [Pg.20]    [Pg.265]    [Pg.422]    [Pg.301]    [Pg.296]    [Pg.884]    [Pg.1754]    [Pg.1755]    [Pg.179]    [Pg.128]    [Pg.242]    [Pg.428]    [Pg.336]    [Pg.146]    [Pg.601]    [Pg.950]    [Pg.100]    [Pg.231]    [Pg.418]    [Pg.793]    [Pg.849]    [Pg.190]    [Pg.366]    [Pg.599]   
See also in sourсe #XX -- [ Pg.250 ]




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