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Environmental pollution studies

O.M. Kvalheim, K. 0ygard and O. Grahl-Nielsen, SIMCA multivariate data analysis of blue mussel components in environmental pollution studies. Anal. Chim. Acta, 150(1983) 145-152. [Pg.241]

U.S. Environmental Protection Agency (USEPA). 1972. Helena Valley, Montana, area environmental pollution study. U.S. Environ. Protection Agency Rep. AP-91. 179 pp. Avail, from U.S. Environ. Protection Agency, Office of Air Programs, Research Triangle Park, NC 27711. [Pg.343]

The high sensitivity of activation analysis has made it very useful in environmental pollution studies. Table 9.2 lists the limits of detection for some elements in sea water under the conditions specified in the table. [Pg.254]

The first task of the specialist in environmental pollution studies is identification of the chemical substances that cause deleterious effects. This is followed by an effort to identify the pathways by which these substances have reached their locus of action, to find their sources, and finally to eliminate or minimize those sources. The tools for identification and measnrement of the amounts of such substances are those of analytical chemistry, namely, spectroscopy, mass spectrometry, gas and liquid chromatography, differential thermal analysis, and neutron activation analysis. These snbjects are discussed fully elsewhere in this encyclopedia. [Pg.202]

Our discussion of radionuclide techniques associated with environmental-pollution studies will be restricted to pesticide studies of an ecological nature. We have decided to emphasize pesticides because their application in the environment has been of significant concern to ecologists for many years. Readers interested in other environmental pollutants are referred to the references cited above. [Pg.218]

Miscellaneous Reactions. Ethylene oxide is considered an environmental pollutant. A study has determined the half-life of ethylene oxide ia the atmosphere (82,83). Autodecomposition of ethylene oxide vapor occurs at - 500° C at 101.3 kPa (1 atm) to give methane, carbon monoxide, hydrogen, and ethane (84—86). [Pg.454]

Fig. 12-2. NO-NO2-O3 ambient concentration profiles from average of four Regional Air Monitoring Stations (RAPS) in downtown St. Louis, Missouri (USA) on October 1, 1976. Source RAPS, Data obtained from the 1976 data file for the Regional Air Pollution Study Program. U.S. Environmental Protection Agency, Research Triangle Park, NC, 1976. Fig. 12-2. NO-NO2-O3 ambient concentration profiles from average of four Regional Air Monitoring Stations (RAPS) in downtown St. Louis, Missouri (USA) on October 1, 1976. Source RAPS, Data obtained from the 1976 data file for the Regional Air Pollution Study Program. U.S. Environmental Protection Agency, Research Triangle Park, NC, 1976.
Data obtained from the 1976 data file of the Regional Air Pollution Study Program. U.S Environmental Protection Agency, Research Triangle Park, NC, 1976. [Pg.177]

Martin, D. J., and Michaelis. (1992). Research and Technology Strategy to Help Overcome the Environmental Problems in Relation to Transport Global Pollution Study. Luxembourg EEC. [Pg.975]

Many pharmaceuticals and environmental pollutants are aromatic amines. Like phenols, this class of compound is generally oxidizable at carbon electrodes. LCEC has been used to study the metabolism of aromatic amines of both environmental and pharmaceutical origin lcec has also been used for the trace determination... [Pg.25]

Rosenblatt DH, Miller TA, Dacre JC, et al. 1975a. Problem definition studies on potential environmental pollutants. I. Toxicology and ecological hazards of 16 substances at the RMA. Technical Report 7508. U.S. Army Medical Bioengineering Research and Development Laboratory, Fort Detrick, Frederick, MD. [Pg.153]

Bergman and Meyer121 point out a particularly relevant problem with mathematical models. The relative reliability of mathematical models (compared with physical models based on empirical field or laboratory studies) decreases rapidly as the number of environmental pollutants being modeled increases (see Figure 20.8). Consequently, mathematical models tend to be less cost-effective for complex wastestreams than physical (empirical) models. [Pg.826]

To obtain the mass emissions of pollutants from e-waste recycling processes, it is essential that the inputs of pollutants are truly e-waste related. To fulfill this requirement, a causal analysis is desirable. However, the concept of causation is rather problematic because causal mechanisms are complex [26]. Nonetheless, we are compelled to identify causes, in an attempt to minimize the uncertainties associated with our estimates. In this chapter, the strict empiricist, David Hume s empirical criterion, was adopted. This approach requires only a combination of (1) e-waste processing and environmental pollution are associated in space and time (contiguity) (2) e-waste processing precede to environmental pollution (temporal succession) and (3) e-waste processing is always conjoined with environmental pollution (consistent conjunction). These are always the cases judged from a number of previous studies [6, 27-35]. [Pg.282]

The method can successfully be used in analyses of impurities in metals and alloys, for estimation of minor elements in monomolecular films of oxide layers of Fe-Cr-Ni alloys, for detection of metal impurities in environmental pollution, for studying the depression of high-grade semiconducting materials and for analysis of the corrosion products of contact junction diodes used in microelectronic circuits. Much sophistication is desirable on the instrumental side so as to incorporate an automatic recording device to make an FR polarograph suitable for wider applications and common use. [Pg.249]

Clinical studies of effective intestinal permeability (Peff), secretion and metabolism of various compounds, such as drugs, environmental pollutants and nutrients are... [Pg.160]


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See also in sourсe #XX -- [ Pg.211 ]

See also in sourсe #XX -- [ Pg.211 ]




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