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Sampling scale

This monitoring framework should be apphed across broad geographic regions. This book recommends a national or (preferably) continental scale of assessment. The data collected in the United States shonld also be comparable, to the extent feasible and appropriate, with other North American and global mercury monitoring efforts, particularly monitoring of atmospheric transport and deposition. [Pg.199]

Ecosystem Responses to Mercuty Contamination Indicators of Change [Pg.200]

Indicator Location (intensive, cluster, or both) Frequency [Pg.200]

Soil (THg and MeHg) Intensive Once to characterize pools [Pg.200]

Instantaneous sediment methylation rate Intensive Biannual [Pg.200]


Today, the use of CHIRBASE as a tool in aiding the chemist in the identification of appropriate CSPs has produced impressive and valuable results. Although recent developments diminish the need for domain expertise, today the user must possess a certain level of knowledge of analytical chemistry and chiral chromatography. Nevertheless, further refinements will notably reduce this required level of expertise. Part of this effort will include the design of an expert system which will provide rule sets for each CSP in a given sample search context. The expert system will also be able to query the user about the specific requisites for each sample (scale, solubility, etc.) and generate rules which will indicate a ranked list of CSPs as well their most suitable experimental conditions (mobile phase, temperature, pH, etc.). [Pg.122]

Critelli, S., Le Pera, E., Ingersoll.R.V. 1997.The effects of source lithology, transport, deposition and sampling scale on... [Pg.464]

Two questions arise from this result. Do lobsters use only chemical and not mechanosensory information, and why do lobsters not use ground reference and head up-current Since turbulent odor dispersal is based on water flow patterns, we must investigate the role of microflow patterns in plume orientation behavior. As for ground reference, we speculate that the flow patterns of the lobster s natural environment may be too complex to allow for efficient rheotactic behavior in odor source localization. This complexity is most likely caused by a mismatch between turbulent scales and animal body size and sampling scales. [Pg.162]

First, the range of separation. The experimentally determined tip-sample separation is 1-4 A before a mechanical contact (Diirig et al. 1988). For most metals, the normal nucleus-nucleus distance of a mechanical contact is 2.5-3 A. Therefore, on the absolute tip-sample scale, it is 3.5-7 A. By comparing with the case of H2, we notice that this is the range where the resonance interaction dominates. In other words, under normal STM operation conditions, over a distance range of about 3 A, resonance energy is almost solely responsible to the atomic force, and the distance dependence of the force should be approximately exponential. [Pg.185]

Table 5 Sample Scale-Up Calculation for a Chromatography Step... [Pg.153]

As part of the material balance review, it is necessary to regularly and frequently undertake water sampling and analysis. From time to time, microbiological samples, scales, or other materials may also need to be analyzed. The questions of how to sample and what water sources to sample... [Pg.369]

A common mistake is to use too little perchloric acid even with acid soluble materials posing no particular difficulty, there is considerable energy given off during the actual perchloric oxidation, and the acid is both consumed as oxidant and vigorously boiled off. If the total amount of acid available is insufficient, the mixture will go to dryness before the oxidation is complete and the dry residues will catch fire. True explosions on the 1—2 g sample scale are rare at this stage, but the beaker may shatter because of the thermal shock, and in any case the analysis will be ruined. [Pg.42]

Apparatus Type of sampler Method of sampling Scale Advantages Disadvantages... [Pg.2962]

The critical issue is that the evaluation scheme should be decided before the collection of field data or the initiation of toxicity tests. Some types of evaluation schemes may require very specific sampling in order to produce the required statistical power. At a regional scale, a sampling scale that ensures an efficient use of resources is critical to prevent the depletion of resources. [Pg.395]

Fig. 2. Schematic representation of conformational space exploration efficiencies and their dependency for the different sampling scale with, insufficient (A), nearly sufficient (B), and almost sufficient (C) number of initial structures. In this example, preliminary calculations are distance geometry or torsion angle space algorithms, and refinement is restraint molecular dynamics with same set of NMR-derived structural information. The exploration extents of the refinements are assumed to be similar for selected preliminary calculation s results (i.e., initial structures of the refinement calculations). Fig. 2. Schematic representation of conformational space exploration efficiencies and their dependency for the different sampling scale with, insufficient (A), nearly sufficient (B), and almost sufficient (C) number of initial structures. In this example, preliminary calculations are distance geometry or torsion angle space algorithms, and refinement is restraint molecular dynamics with same set of NMR-derived structural information. The exploration extents of the refinements are assumed to be similar for selected preliminary calculation s results (i.e., initial structures of the refinement calculations).
The review is organized as follows first, we discuss aspects of the unitary approach for combining adsorptive and capillary contributions, and present the new pore scale model of Tuller et al. (1999). The upscaling scheme of Or and Tuller (1999) for representing sample scale retention properties will be presented, followed by illustrative examples with measured characteristic data and a discussion of critical soil parameters. The role of liquid-vapor interfacial area will be highlighted by comparisons of model predictions with limited measurements. Finally, we introduce hydrodynamic considerations of unsaturated flow in films and comers leading to prediction of hydraulic conductivity of rough rock surfaces and unsaturated porous media. [Pg.3]

Upscaling Considerations From Pore- to Sample Scale... [Pg.16]

The upscaling scheme was applied lo Ihe pore scale model based on the SYL formulation, leading to Ihe development of closed-form expressions for sample scale... [Pg.17]

Sample Scale Liquid-Vapor Interfacial Area... [Pg.21]

Specific Surface Area Constraint. An important requirement for model parameter estimation is that calculated sample scale specific surface area should be within 90% of independently measured surface area. A 90% limit was chosen based on the relatively large uncertainty in most standard methods for surface area measurements [e.g., EGME method (Carter et al., 1986)]. The sample scale expected value of specific surface area SAe is calculated according to ... [Pg.22]


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See also in sourсe #XX -- [ Pg.196 , Pg.199 , Pg.200 ]




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B Sample Cyclone Scaling Calculations

Sample application preparative scale

Sampling time scales

Scale sample calculation

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