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INDEX sediments

Cloud point Pour point Neutralization index Sediment content... [Pg.302]

Strontium Sulfate. Strontium sulfate, SrSO, occurs as celestite deposits in beds or veins in sediments or sedimentary rocks. Celestite has a specific gravity of ca 3.97, a Mohs hardness of 3.0—3.5, and is colodess-to-yeUow and often pale blue. Strontium sulfate forms colorless or white rhombic crystals with a specific gravity of 3.96 and an index of refraction of 1.622—1.631. It decomposes at 1580°C and has a solubiUty of 0.0113 g per 100 mL of water at 0°C. [Pg.475]

Molecular weights of polysaccharides in solution can also be measured by osmotic pressure and light scattering. Osmotic pressure yields the number average molecular weight, which can be usefully used with Mw from sedimentation equilibrium as a measure of polydispersity Preston and Wik [28] have done this for example with hyaluronic acid. The ratio Mw/Mn the polydispersity index is often given as a measure of polydispersity, and can be related to the width of a molecular weight distribution via the well-known Herdan [96] relation ... [Pg.234]

Tables Sedimentation coefficient ratio. (Scomplex (Based on data from [138,140,143,145]) /Smucin) as an index of adhesiveness... Tables Sedimentation coefficient ratio. (Scomplex (Based on data from [138,140,143,145]) /Smucin) as an index of adhesiveness...
It is essential that the solution be sufficiently dilute to behave ideally, a condition which is difficult to meet in practice. Ordinarily the dilutions required are beyond those at which the concentration gradient measurement by the refractive index method may be applied with accuracy. Corrections for nonideality are particularly difficult to introduce in a satisfactory manner owing to the fact that nonideality terms depend on the molecular weight distribution, and the molecular weight distribution (as well as the concentration) varies over the length of the cell. Largely as a consequence of this circumstance, the sedimentation equilibrium method has been far less successful in application to random-coil polymers than to the comparatively compact proteins, for which deviations from ideality are much less severe. [Pg.307]

A global sensitivity analysis was performed for the lead concentration in the arterial blood model (Fig. 7) over the simulation period for each parameter. Parameters considered for the sensitivity analysis are listed in Table 8 (Annex 1). The magnitude of sensitivity is shown by relative sensitivity index. It was observed that the most influential parameter is the porosity of the sediment of the river (phi sed)... [Pg.368]

Figure 8-2 shows the depth profiles of the saturation index omegadel), the solution rate, and the respiration rate. At the shallowest depths, the saturation index changes rapidly from its supersaturated value at the sediment-water interface, corresponding to seawater values of total dissolved carbon and alkalinity, to undersaturation in the top layer of sediment. Corresponding to this change in the saturation index is a rapid and unresolved variation in the dissolution rate. Calcium carbonate is precipitating... [Pg.156]

National Uranium Resource Evaluation (NURE) Hydrochemical and Stream Sediment Reconnaissance (HSSR) Program. U.S. Geological Survey Open-File Report 97-492. Available from . [Pg.172]

Fig 4. Multiplicative Au Ag index for catchment outlet sediment samples after MMI extraction. [Pg.234]

Once interpenetration occurs the resistance to deformation increases markedly, so for example we would expect compaction of a sediment to become limited, as would further concentration in a filter press. It is worth emphasising the point that this is a simplistic approach, as prior to interpenetration the clusters undergo structural rearrangements changing their fractal index at a critical volume fraction. A typical data set for yield stress is shown in Figure 6.16.19... [Pg.249]

Figure 5.17. Sedimentation index n as function of Galileo number Ga (from equation 5.84)... Figure 5.17. Sedimentation index n as function of Galileo number Ga (from equation 5.84)...
Equation 6.31 is similar to equation 5.71 for a sedimenting suspension. Values of the index n range from 2.4 to 4.8 and are the same for sedimentation and for fluidisation at a given value of the Galileo number Ga. These may be calculated from equation 6.32, which is identical to equation 5.84 in Chapter 5 ... [Pg.303]

Mineral data from Mindat.org (www.mindat.org/index.php). Sediments data from Hamilton, L. (1976). Journal of Sedimentary Petrology 46, 2, 280-300. [Pg.336]

Fig. 8.47 Phenanthrene adsorption-desorption hysteresis observed for Lachine and Chelsa humic acid aggregate the hysteresis index is given by n. Reprinted from Huang W, Peng, P. Yu, Z. and Fu J (2003) Effects of organic matter heterogeneity on sorption and desorption of organic contaminants by soils and sediments. Appl Geochem 18 955-972. Copyright 2003 with permission of Elsevier... Fig. 8.47 Phenanthrene adsorption-desorption hysteresis observed for Lachine and Chelsa humic acid aggregate the hysteresis index is given by n. Reprinted from Huang W, Peng, P. Yu, Z. and Fu J (2003) Effects of organic matter heterogeneity on sorption and desorption of organic contaminants by soils and sediments. Appl Geochem 18 955-972. Copyright 2003 with permission of Elsevier...
The type of measurements that are needed to accomplish the task should also be considered. Refractive index values are generally needed for measurements based on light scattering. Densities are often needed for techniques based on acoustics and sedimentation. Further, most approaches require the samples to be dissolved or suspended in a liquid. Thus, information related to how the liquid affects particle shape and association is also important. [Pg.452]

Absolute methods provide the molecular weight and the degree of polymerization without any calibration. Their calculation from the experimental data requires only universal constants such as the gas constant and Avogadro s number, apart from readily determinable physical properties such as density, refractive index, etc. The most important methods in use today are mass spectrometry, osmometry, light scattering, and - to some extent - sedimentation and diffusion measurements. Also, some chemical and spectroscopic methods (determination of end-groups) are important because of their relative simplicity. [Pg.92]

In one example, the colloidal structure, is made by sedimentation of polystyrene beads, giving voids in the range 120-1000 mn, and the voids are filled with TiO generated from titanium tetrapropoxide. The polystyrene bead lattice is then removed by calcining to give an iridescent material, but not with a full photonic band gap. In this case one of the controlling factors is the refractive index of the matrix, which needs to be greater than 2.8. [Pg.352]

In a local impact assessment (Box C), the predicted intersex (expressed as PAF) is compared with the actual occurring intersex (Schipper et al. 2008a). In the local sediments of the harbours, there is a good correlation between the predicted risk and the observed Intersex Index (ISI). No toxic effects were observed at the disposal sites for dredged sediments Loswal Noord (Table 2) and in the North Sea (Stronkhorst et al., 2003a). However, along the Dutch coast, the... [Pg.104]

Table 5 Example application of process in Box B to evaluate the risk of TBT in Dutch sediments and biota. Ecotoxi-cologjcal risk determined as potentially affected fraction (PAF %) based on the sediment levels interpolated in the SSD for TBT (from Schipper et al., 2008a), in the field observed intersex index (ISI) values in periwinkle L. littorea and Vas Deferens Sequence Index (VDSI) in dogwheUc N. lapillus as biomarkers for TBT-exposure (unpublished own results). Based on a combination of the criteria ISI<0.3, VDSI>1 and TBT-PAF<10%, the risk status of the sediments is classified (last column). Table 5 Example application of process in Box B to evaluate the risk of TBT in Dutch sediments and biota. Ecotoxi-cologjcal risk determined as potentially affected fraction (PAF %) based on the sediment levels interpolated in the SSD for TBT (from Schipper et al., 2008a), in the field observed intersex index (ISI) values in periwinkle L. littorea and Vas Deferens Sequence Index (VDSI) in dogwheUc N. lapillus as biomarkers for TBT-exposure (unpublished own results). Based on a combination of the criteria ISI<0.3, VDSI>1 and TBT-PAF<10%, the risk status of the sediments is classified (last column).
Some of the more critical properties related to marine fuels include ash content, carbon residue, calculated carbon aromaticity index (CCAI), density, sulfur, total sediment, and viscosity. A description of these properties and the primary reason for their implementation are provided below ... [Pg.63]


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See also in sourсe #XX -- [ Pg.149 , Pg.162 , Pg.163 , Pg.169 , Pg.181 ]

See also in sourсe #XX -- [ Pg.149 , Pg.162 , Pg.163 , Pg.169 , Pg.181 ]




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