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Mobility cadmium compounds

The chemical basis of this time period may not be uniform for all of the type b metals. For mercury(II) it appears to be related to the occurrence of a minimum amount of what is literally the destruction of tissue and proteins. In the case of cadmium it appears to have a different basis at least in part. Subsequent to the injection of an otherwise lethal dose of a cadmium compound there is a relatively short period when it can be complexed and removed and the animal saved. As the interval between the cadmium injection and that of the antidote (e.g. CaEDTA or CaDTPA) increases, the cadmium becomes more and more difficult to mobilize and a point is soon reached where the antidote is without effect ( 5). In the same fashion, aged cadmium deposits are apparently resistant to mobilization by EDTA ). [Pg.336]

Table 4.1-166 Electron and hole mobilities /Un and /tp of cadmium compounds... Table 4.1-166 Electron and hole mobilities /Un and /tp of cadmium compounds...
The most common toxic metals in industrial use are cadmium, chromium, lead, silver, and mercury less commonly used are arsenic, selenium (both metalloids), and barium. Cadmium, a metal commonly used in alloys and myriads of other industrial uses, is fairly mobile in the environment and is responsible for many maladies including renal failure and a degenerative bone disease called "ITA ITA" disease. Chromium, most often found in plating wastes, is also environmentally mobile and is most toxic in the Cr valence state. Lead has been historically used as a component of an antiknock compound in gasoline and, along with chromium (as lead chromate), in paint and pigments. [Pg.177]

Cadmium is found naturally deep in the subsurface in zinc, lead, and copper ores, in coal, shales, and other fossil fuels it also is released during volcanic activity. These deposits can serve as sources to ground and surface waters, especially when in contact with soft, acidic waters. Chloride, nitrate, and sulfate salts of cadmium are soluble, and sorption to soils is pH-dependent (increasing with alkalinity). Cadmium found in association with carbonate minerals, precipitated as stable solid compounds, or coprecipitated with hydrous iron oxides is less likely to be mobilized by resuspension of sediments or biological activity. Cadmium absorbed to mineral surfaces (e.g., clay) or organic materials is more easily bioaccumulated or released in a dissolved state when sediments are disturbed, such as during flooding. [Pg.63]

The solid nitrate absorbs dry ammonia, yielding a colourless mobile liquid, the composition varying with the temperature and pressure. The product is known as Divers s liquid, and appears to consist of solutions of ammonium nitrate and ammonia in one another. In its chemical behaviour this liquid resembles liquid ammonia. It dissolves bromine with liberation of nitrogen, and is converted by iodine into a solid mass, possibly Millon s compound, N2H6I2. It dissolves potassium, sodium, magnesium, zinc, and cadmium, the nitrate being reduced to nitrite.13... [Pg.234]

Human activities often mobilize and redistribute natural compounds in the environment to an extent that they can cause adverse effects. Much attention has been paid to the determination of trace of pollutant elements on account of their significant effect on the environment. The potential of USAL has been put into use in environmental element analysis. Thus, the US leaching of cadmium from coals and pyrolysed oil shale prior to ETAAS [56] resulted in a twofold increase in precision, better detection limits and decreased background absorbance in relation to total digestion. Cadmium has also been successfully leached with US assistance from ash samples with subsequent flow-injection coid-vapour atomic absorption spectrometry [57]. Additional examples include the leaching of germanium from soiis with an uitrasonic probe in 10 min [58] or that of lead from coal in 60 s [59]. [Pg.125]

Certain acid dyes [67] stabilize silver oxalate by forming surface compounds, while other dyestufis accelerate the decomposition because their redox properties enhance the ease of electron transfer from the oxalate ion to the silver. The influences of incorporated cadmium, copper and other ions on the rate of thermal decomposition, and on the concentration and mobility of interstitial silver ions, have been reviewed [46,68]. [Pg.457]

F) Preparation and Testing of Candidate Structures. Suitable candidate structures were then examined for relative efficacy in the mobilization of lead from lead-loaded mice. On the basis of previous studies in which we examined the relative ability of many compounds to remove cadmium from its aged deposits in the liver and the kidneys, six vicinal dithiols were selected, which were all monoesters of meso-2,3-dimercaptosuccinic acid. The compounds selected were the mono esters of meso- 2,3-dimercaptosuccinic acid with the following alcohols n-propyl, wo-propyl, n-butyl, wo-butyl, n-amyl, and iso-dmy (Figure 3). The results of experiments comparing these compounds showed that the n-butyl, iso-butyl, n-amyl, and isoamyl monoesters of m j<>-2,3-dimercaptosuccinic acid were the most effective compounds and that all were capable of reducing both kidney and brain lead levels in lead-intoxicated mice (45). The data collected on lead-intoxicated mice treated with the most effective of such compounds are compared with the results obtained with DMSA in Table I. [Pg.435]

CdTe is a crystalline compound with a cubic zinc blende (sphalerite) crystal structure (lattice constant of 6.481 A), a direct band gap of 1.5 eV, an ideal match to the solar spectrum, and an extinction coefficient around 5 x 10" cm . " ° The intrinsic defects include cadmium interstitials and cadmium vacancies, and extrinsic doping can be achieved using In (donor) substitution or Cu, Ag, Au (acceptor) substitution for Cd. The mobilities have been measured to be up to 1100 cm s for electrons and up to 8 cm s for holes. Dopant densities up to 10 cm ... [Pg.109]

Lead-stabilized products, used in some parts of the world in rigid extrusions, often contain 0.4-0.8 phr of calcium stearate as internal lubricant, 0.2-0.5 phr of stearyl alcohol to improve the mobility of the stabilizer (normally dibasic lead phosphate or combinations with tribasic lead sulfate), and 0.4-0.75 phr of partly saponified mon-tanic ester as a multifunctional lubricant. For the ultimate in process stability, calcium stearate may be replaced by a barium/cadmium stearate blend. The inclusion of cadmium also reduces the severity of staining by airborne sulfur compounds. Although lead-stabilized rigid compounds offer advantages in material cost and process safety, their use should be abandoned because of the hazard involved and because such usage is prejudicial to acceptance of vinyl products. [Pg.346]


See other pages where Mobility cadmium compounds is mentioned: [Pg.68]    [Pg.394]    [Pg.397]    [Pg.588]    [Pg.349]    [Pg.215]    [Pg.394]    [Pg.130]    [Pg.93]    [Pg.411]    [Pg.149]    [Pg.345]    [Pg.126]    [Pg.303]    [Pg.252]    [Pg.356]    [Pg.4921]    [Pg.335]    [Pg.13]    [Pg.60]    [Pg.354]    [Pg.346]    [Pg.2111]    [Pg.308]    [Pg.42]    [Pg.703]    [Pg.889]    [Pg.299]    [Pg.45]    [Pg.462]    [Pg.382]    [Pg.331]    [Pg.161]   
See also in sourсe #XX -- [ Pg.682 ]

See also in sourсe #XX -- [ Pg.682 ]




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Cadmium compounds

Cadmium mobilization

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