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Fate pathway

If areas identified as likely to receive significant atmospheric contaminant concentrations include areas supporting edible biota, the biouptake of contaminants must be considered as a possible environmental fate pathway. Direct biouptake from the atmosphere is a potential fate mechanism for lipophilic contaminants. Biouptake from soil or water following transfer of contaminants to these media must also be considered as part of the screening assessments of these media. [Pg.235]

Contaminant transfer to bed sediments represents another significant transfer mechanism, especially in cases where contaminants are in the form of suspended solids or are dissolved hydrophobic substances that can become adsorbed by organic matter in bed sediments. For the purposes of this chapter, sediments and water are considered part of a single system because of their complex interassociation. Surface water-bed sediment transfer is reversible bed sediments often act as temporary repositories for contaminants and gradually rerelease contaminants to surface waters. Sorbed or settled contaminants are frequently transported with bed sediment migration or flow. Transfer of sorbed contaminants to bottomdwelling, edible biota represents a fate pathway potentially resulting in human exposure. Where this transfer mechanism appears likely, the biotic fate of contaminants should be assessed. [Pg.237]

Berger, B.M. and Wolfe, N. L. Hydrolysis and biodegradation of sulfonylurea herbicides in aqueous buffers and anaerobic water-sediment systems assessing fate pathways using molecular descriptors, Anwrort. Toxicol. Chem., 15(9) 1500-1507,1996. [Pg.1632]

Berger, B.M. and Wolfe, N.L. (1996). Hydrolysis and Biodegradation of Sulfonylurea Herbicides in Aqueous Buffers and Anaerobic Water-Sediment Systems. Assessing Fate Pathways Using Molecular Descriptors. Environ.Toxicol.Chem., 15,1500-1507. [Pg.538]

When released into the environment as a vapor, methylene chloride does not usually undergo direct photolysis but does degrade by reaction with photo-chemically produced hydroxyl radicals. Its half-life in the atmosphere is estimated at 119 days. In soil and water, a major fate pathway involves volatilization to the atmosphere and subsequent degradation. Activated sludge studies have, however, demonstrated biodegradation of methylene chloride. Little bioconcentration in aquatic species can be expected. [Pg.1679]

A Henry s law constant of 3.2 x 10" atm-mVmole indicates the potential for significant volatilization from water. However, the rapid rate of hydrolysis may reduce the significance of this fate pathway. [Pg.143]

Man has artificially produced radioelements (technetium, promethium, transuranium elements) and also many radioactive isotopes of the naturally occurring elements. Thus, the natural radioactivity on the earth is to some extent increased by man-made radioactive materials. Many analytical research works focus on the determination of manmade radionuclides, their migration, pathways, and accumulation in the environment. The aim of this analytical research work is either to know about fate, pathway, and metabolism of materials or to obtain information about possible environmental protection problems. [Pg.4113]

Simplified environmental fate estimation procedures are based on the predominant mechanisms of transport within each medium, and they generally disregard intermedia transfer or transformation processes. In general, they produce conservative estimates (i.e., reasonable upper bounds) for final ambient concentrations and the extent of hazardous substance migration. However, caution should be taken to avoid using inappropriate analytical methods that underestimate or overlook significant pathways that affect human health. [Pg.230]

Figures 16-3 through 16-5 present the decision network for screening contaminant fate in air, surface water, ground water, and biota. Pathways must be further evaluated to determine the likelihood of population exposure. Figures 16-3 through 16-5 present the decision network for screening contaminant fate in air, surface water, ground water, and biota. Pathways must be further evaluated to determine the likelihood of population exposure.
Multiple pathways are a major concern since depostion of PIC would have occurred. Specific soil conditions determine attenuation rates of penta PIC leachate. Once penta reaches the water table, other transport and fate processes become important. Penta exists in two forms ionized and non-ionized. The ionized form is soluble in water, while the non-ionized form is not. The ratio of the two forms in water is dependent on the pH of the aquifer. In alkaline environments penta PIC tend to be more soluble and more susceptible to advective transport and biological decay. Half-lives of penta leachate in groundwater have been estimated ranging from 27 days to 58 years. [Pg.337]

The primary fate of acetyl CoA under normal metabolic conditions is degradation in the citric acid cycle to yield C02. When the body is stressed by prolonged starvation, however, acetyl CoA is converted into compounds called ketone bodies, which can be used by the brain as a temporary fuel. Fill in the missing information indicated by the four question marks in the following biochemical pathway for the synthesis of ketone bodies from acetyl CoA ... [Pg.1174]

In order to develop a rational approach to improving rates of metabolite production, it is necessary to consider the fate of the nutrients that are required for its synthesis. However, overcoming the major flux control points within a metabolic pathway may not lead to metabolite overproduction if the energetic consequences of the alteration are unfavourable to the organism. [Pg.36]

The synthesis of virtually all proteins in a cell begins on ribosomes in the cytosol (except a few mitochondrial, and in the case of plants, a few chloroplast proteins that are synthesized on ribosomes inside these organelles). The fate of a protein molecule depends on its amino acid sequence, which can contain sorting signals that direct it to its corresponding organelle. Whereas proteins of mitochondria, peroxisomes, chloroplasts and of the interior of the nucleus are delivered directly from the cytosol, all other organelles receive their set of proteins indirectly via the ER. These proteins enter the so-called secretory pathway (Fig. 1). [Pg.648]

On a global scale, the atmosphere serves as the major pathway for the transport and deposition of contaminants from emission sources to terrestrial and aquatic ecosystem receptors (22, 27). Once a contaminant is airborne, the processes of atmospheric di sion, transport, transformation, and deposition act to determine its fate. These processes are complex and the degree to which they influence the fate of a particular contaminant is dependent on its physico-chemical characteristics, the properties and concentrations of coexisting substances, and the prevailing meteorological conditions, including wind, precipitation, humidity, temperature, clouds, fog, and solar irradiation. [Pg.138]

The high conversion test is operated to ensure that essentially complete conversion of the HBr is possible, and to study the fate of the feed contaminants. In this test, the conditions are selected to ensure complete conversion of the HBr. Several reaction pathways are then available to feed contaminants. They may undergo combustion, react with HBr, or react with the bromine formed. The extent of reaction via any of these pathways will depend on the nature of the contaminants and the temperature. Information concerning the fate of the contaminants can then be gained by analyzing the gas, bromine, and aqueous phases exiting the reactor. [Pg.307]

Figure 20-4. Uronicacid pathway. (Asterisk indicates the fate of carbon 1 ofgiucose ,—POj .)... Figure 20-4. Uronicacid pathway. (Asterisk indicates the fate of carbon 1 ofgiucose ,—POj .)...
Ziegler, L, The pteridine pathway in zebrafish regulation and specification during the determination of neural crest cell-fate, Pigment. Cell Res., 16, 172, 2003. [Pg.120]

The crucial aspect is thus to determine the fate of the ( CHO), species. Possible mechanisms for its oxidative removal are schematically shown in Fig. 9. From this scheme, it appears that the desorption of the formyl species can follow different pathways through competitive reactions. This schematic illustrates the main problems and challenges in improving the kinetics of the electrooxidation of methanol. On a pure platinum surface, step (21) is spontaneously favored, since the formation of adsorbed CO is a fast process, even at low potentials. Thus, the coverage... [Pg.81]


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Environmental Fate and Pathways of Exposure to Chemicals in the Environment

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