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INDEX surface water

Notice, that with these extremely good resolutions in case of surface sensing contamination of the sensitive layer with solid particles has to be avoided completely, e.g. by an appropriate filtering of the sample solutions. Notice also that the temperature coefficient of the refractive index of water is about 10-4 per °C. So if applying the surface sensing mode using watery solutions indeed a perfect balance of both branches and low temperature gradients have to be aimed at. [Pg.273]

Taylor et al. conducted DFT simulations using a periodic model of the interface between water and various metal surfaces with an index of (1 1 l).102 The chemistry of water at these charged interfaces was investigated and the parameters relevant to the macroscopic behavior of the interface, such as the capacitance and the potential of zero charge (PZC), were evaluated. They also examined the influence of co-adsorbed CO upon the equilibrium potential for the activation of water on Pt(l 1 1). They found that for copper and platinum there was a potential window over which water is inert. However, on Ni(l 1 1) surface water was always found in some dissociated form (i.e., adsorbed OH or H ). The relaxation of water... [Pg.357]

Application of the EDAR Index to a case study of surface water and groundwater pollution... [Pg.239]

Morrall2 used a HPLC system with two columns. The first column was loaded with the controlled pore glass (CPG) to be modified. The second column was used for separation of the reaction effluents. This column was coupled to a refractive index detector, allowing for quantitative detection of the effluents. The reaction was initiated by injecting an APTS/toluene mixture and stopped by injection of pure toluene. With this so-called stop-flow mechanism reaction times down to 18 seconds could be used. From these analyses it became evident that upon mixing of the aminosilane with the silica, a very rapid physisorption occurs. The initial adsorption of the APTS (from toluene solution on dried CPG) occurred before the 18 second minimum time delay of the stop-flow apparatus. For non-aminated silanes the adsorption proved to be much slower. This study also revealed the pivotal role of surface water in the modification of siliceous surfaces with alkoxysilanes, as discussed in the previous chapter. [Pg.210]

Surface water temperature is approximately 32°C throughout the year. Water temperature is 34.25°C at a depth of 51 meters (R.J. Hoffman, U.S. Geological Survey, 1990, personal communication). Water in Devils Hole is slightly supersaturated with respect to calcite (saturation index averages about 0.18) with calculated Pco2 values from 0.0123 to 0.0141 atm (Plummer et al., 2000). The water has been supersaturated with calcite for at least 500,000 years. [Pg.230]

Instrument used (measured response) Dia-Stron erythema meter , Minolta Chromameter , Cortex Dermaspectrometer (all measure a redness index of erythema) laser Doppler Velocimeter (blood flow) Servo-Med evaporimeter (transepidermal or skin surface water loss)... [Pg.2443]

For evaluating pollution, data is taken from the state network monitoring the quality of surface water operated by the Czech Hydrometeorological Institute based on several indicators (BOD5, N-NH4, N-NOG, Ptotal and the saprobic index of macrozoobenthos). [Pg.96]

Pratt, L., Pavanello, R. and Pesarin, F. (1971) Assessment of surface water quality by a single index of pollution. Water Research, 5(9), 741-751. [Pg.128]

Siderite and rhodocrosite may approach saturation when acid mine waters are neutralized by contact with carbonate rocks. Figure 6.18 shows the trend toward saturation with respect to carbonate minerals of some surface waters and groundwaters affected by bituminous coal mining (Gang and Langmuir 1974). Plotted are the saturation indices of various metal carbonates versus the index for calcite. The plots show that siderite and rhodocrosite reach equilibrium in some streams (probably because of CO2 loss), whereas calcite and the other carbonates remain undersaturated in all samples. [Pg.219]

When the overall oxidation state of a system is desired, unless a water is obviously anaerobic (e.g., it has an H2S odor) one should first attempt to measure dissolved oxygen as an index of system redox state. Eh measurements are unlikely to be stable and thermodynamically meaningful in surface-waters, except in acid waters (where ferrous and ferric species are usually present). Eh measurements may be stable and meaningful in anaerobic sediments or groundwaters, when species of iron, sulfur, and manganese dominate the redox chemistry, but otherwise are of qualitative value only. [Pg.414]


See other pages where INDEX surface water is mentioned: [Pg.108]    [Pg.392]    [Pg.209]    [Pg.118]    [Pg.45]    [Pg.300]    [Pg.647]    [Pg.137]    [Pg.30]    [Pg.47]    [Pg.109]    [Pg.193]    [Pg.244]    [Pg.245]    [Pg.245]    [Pg.362]    [Pg.237]    [Pg.240]    [Pg.641]    [Pg.642]    [Pg.656]    [Pg.366]    [Pg.301]    [Pg.13]    [Pg.14]    [Pg.37]    [Pg.79]    [Pg.195]    [Pg.91]    [Pg.209]    [Pg.579]    [Pg.56]    [Pg.2164]    [Pg.3257]    [Pg.3259]    [Pg.3274]    [Pg.572]    [Pg.201]    [Pg.429]    [Pg.220]    [Pg.121]   
See also in sourсe #XX -- [ Pg.7 , Pg.32 , Pg.85 , Pg.91 , Pg.115 , Pg.118 , Pg.119 , Pg.123 , Pg.125 , Pg.134 , Pg.174 , Pg.209 , Pg.216 , Pg.223 , Pg.234 , Pg.237 , Pg.239 , Pg.247 , Pg.282 , Pg.307 ]




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INDEX surface

INDEX water

Subject index surface water

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