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Cadmium iron absorption

Since the kidneys are the main depot for cadmium, they are of greatest concern for cadmium toxicity. Cadmium interferes with the proximal tubule s reabsorption function. This leads to abnormal actions of uric acid, calcium, and phosphorus. Amino aciduria (amino acids in the urine) and glucosuria (glucose in the urine) result in later stages, proteinuria (protein in the urine) results. When this happens, it is assumed that there is a marked decrease in glomerular filtration. Long-term exposure to cadmium leads to anemia, which may result from cadmium interfering with iron absorption. [Pg.376]

Hamilton, D.L. and L.S. Valberg. 1974. Relationship between cadmium and iron absorption. Am.. Physiol. 227 1033-1037. [Pg.231]

Data concerning the toxicity of the four discussed toxic minerals are presented in Tables 4.5 and 4.6. The uptake of elements is not entirely independent of one another. Elements of similar chemical properties tend to be taken up together. Sometimes one element has an inhibiting effect on another, or there can be a synergistic effect, e.g., enhancement of absorption of calcium in the presence of adequate amounts of phosphorus, or cadmium and lead hindering calcium and iron absorption, or zinc and copper antagonism and their influence on the ratio of Zn/Cu on copper deficiency. [Pg.77]

Chemical analysis provides much more precise data about the sample, particularly the determination of metallic elements, mainly lead, cadmium, iron, calcium, sodium as well a.s anions, chlorides, fluorides, nitrates, carbonates and sulphates. The analyses are performed most frequently by spectrophotometry, atomic absorption spectrometry, or polarography in recent years radionuclide X-ray fluorescence and activation analysis have been used. [Pg.596]

Several methods have been reported for concentrating lead, cobalt, and nickel in blood, urine, brines, and water prior to final determination by atomic absorption. Sprague and Slavin (6) described a procedure for determining these elements plus copper, cadmium, iron, and manganese in concentrated potassium chloride solutions. The metals were chelated with ammonium pyrrolidine dithiocarbamate (APDC) and extracted with methyl isobutyl ketone (MIBK). It was reported that the optimum pH for the extraction was approximately 2.8. Berman (J) described a similar chelation-extraction procedure for determining lead in urine and blood. Burrell (2) developed a procedure for determining cobalt and nickel in natural waters by atomic absorption in which both metals are first coprecipitated with ferric chloride from ten liters of water. The separated precipitate is subsequently dissolved and made up to 100 ml. volume with hydrochloric acid and water so that the final pH of the solution is 2.5. The nickel and cobalt are then chelated with APDC and extracted with three 10 ml. volumes of MIBK. Three extractions are necessary to achieve complete recovery of the chelated cations. A detection limit of 0.3 fig. of nickel per liter and 0.15 fig. of cobalt per liter was found. [Pg.231]

Chromium-zinc mixtures were more-than-additive in toxicity to Tisbe holothuriae, a marine copepod. Zinc in combination with chromium was more toxic to copepods than were mixtures of zinc with copper, lead, nickel, or cadmium. Renal tubular absorption of zinc in mice was impaired by certain diuretics and was further influenced by dietary proteins. Zinc absorption in rats was depressed after consumption of high levels of inorganic iron absorption was normal with organoirons. Mercury-zinc mixtures were more-than-additive in toxicity to... [Pg.850]

Chakraborti et al. [665] determined cadmium, cobalt, copper, iron, nickel, and lead in seawater by chelation with diethyldithiocarbamate from a 500 ml sample, extraction into carbon tetrachloride, evaporation to dryness, and redissolution in nitric acid prior to determination by electrothermal atomic absorption spectrometry in amounts ranging from 10 pg (cadmium) to 250 pg (nickel). [Pg.239]

Mykytiuk et al. [184] have described a stable isotope dilution sparksource mass spectrometric method for the determination of cadmium, zinc, copper, nickel, lead, uranium, and iron in seawater, and have compared results with those obtained by graphite furnace atomic absorption spectrometry and inductively coupled plasma emission spectrometry. These workers found that to achieve the required sensitivity it was necessary to preconcentrate elements in the seawater using Chelex 100 [121] followed by evaporation of the desorbed metal concentrate onto a graphite or silver electrode for isotope dilution mass spectrometry. [Pg.287]

The elements covered are aluminium, cadmium, chromium, cobalt, copper, iron, lead, manganese, nickel, vanadium, and zinc. Electrothermal atomic absorption and anodic and cathodic scanning voltammetric methods are discussed. [Pg.338]

Cadmium is a widely distributed metal used in manufacturing and is present in a number of consumer products. Dietary exposure to cadmium is possible from shellfish and plants grown on cadmium-contaminated soils. Absorption is increased when associated with low levels of iron or calcium in the diet. Some plants, such as tobacco, can concentrate cadmium from even low levels in the soil. The lung readily absorbs cadmium, thus cigarette smokers have elevated cadmium exposure. Cadmium is also used as a metal alloy, in paint, and in batteries (Ni-Cad, nickel-cadmium). Workplace exposure can occur in welding and battery manufacture. [Pg.127]

The application of inductively coupled plasma atomic emission spectrometry and graphite furnace atomic absorption spectrometry to the determination of cadmium (and molybdenum) in soils has been discussed by Baucells et al. [53]. Baucells et al. chose the 228.802 nm cadmium line because it is well resolved from the 228.763 nm iron line with the spectrometer used in this work. Background measurements could only be carried out at +0.05 nm. These workers obtained good agreement between cadmium values obtained by direct graphite furnace atomic absorption spectrometry and inductively coupled plasma atomic emission spectrometry. Chelation extraction procedures that require extensive sample handling are avoided. [Pg.35]

A saturation effect is indicated in that iron enhances identically the cadmium inhibitory effect upon manganese absorption irrespective of the cadmium dose. In addition, the iron dose does not alter only the already strong effect of high cadmium dose. Furthermore, within a span of 5.0-15.0 mg Fe/100 ml iron has an equal effect upon cadmium action, while below 2.5 mg Fe/100 ml it does not alter the effect of cadmium at all. This is yet another indication of iron saturation at a level above 5.0 mg Fe/ml milk, as observed earlier (83). [Pg.74]

A plausible rationalization would be that there is a competition for the transport route through the intestinal wall between cadmium and manganese on the one side, and between iron and manganese on the other. The competition, i.e., absorption in the intestinal tract, depends upon the relative concentration of these ions and kinetics of and affinity for their interaction with the binding sites in the intestinal mucosa. [Pg.75]

This method is for the determination of cadmium, cobalt, copper, iron, manganese, nickel, lead and zinc, which are solvent extracted and concentrated as their diethyldithiocarbamate chelates. After destruction of the organic complexes dissolution of the residue in dilute acid gives a solution suitable for atomic absorption analysis [13]. [Pg.276]

Interactions Overabundance of one trace element can interfere with the metabolic use of another element available at normal levels. For example, addition of large amounts of zinc to a diet interferes with (antagonizes) intestinal copper absorption, resulting in copper deficiency from a diet with adequate copper content. Copper deficiency can provoke iron deficiency and anaemia. Molybdenum deficiency in animals can be induced by co-administration of large amounts of the similar element tungsten. Iron deficiency can also increase retention of cadmium and lead, and selenium has been proposed to protect against cadmium and mercury toxicity. [Pg.60]

ALCOHOL MINERALS Regular intake of alcohol could cause depletion of iron, zinc, magnesium and selenium. Alcoholic drinks such as wine and whisky may have high or potentially toxic contents of the toxic element cadmium Attributed to l absorption or L intake of nutrients Be a ware. Monitor cadmium levels as well as plasma levels of other minerals... [Pg.718]

Official Methods of Analysis of AOAC International 17th edn. Rev 1, AOAC International, Gaithersburg, MD, USA, Official Method 999.10. Lead, Cadmium, Zinc, Copper, and Iron in Foods - Atomic Absorption Spectrophotometry after Microwave Digestion (2002)... [Pg.223]

Colored pigments the optical effect is caused by selective light absorption and also to a large extent by selective light scattering (examples iron oxide red and yellow, cadmium pigments, ultramarine pigments, chrome yellow, cobalt blue)... [Pg.8]

Gastrointestinal absorption, and subsequent utilization and retention by the body, of essential trace elements such as zinc, copper, and selenium can also be enhanced or diminished by the presence or absence of other trace elements and chemicals in the diet (WHO, 1996). For example, cadmium and lead absorption is enhanced when dietetic intake of calcium, iron, and phosphate is low. Phytate, an organic phosphate that is abundant in diets high in unrefined grains, especially when accompanied by high dietetic calcium, helps suppress the uptake of potentially toxic elements such as lead and cadmium, but also inhibits the uptake of essential zinc (WHO, 1996). [Pg.4815]


See other pages where Cadmium iron absorption is mentioned: [Pg.121]    [Pg.1563]    [Pg.450]    [Pg.112]    [Pg.255]    [Pg.344]    [Pg.245]    [Pg.259]    [Pg.58]    [Pg.244]    [Pg.319]    [Pg.390]    [Pg.58]    [Pg.244]    [Pg.9]    [Pg.34]    [Pg.102]    [Pg.493]    [Pg.428]    [Pg.74]    [Pg.81]    [Pg.314]    [Pg.416]    [Pg.424]    [Pg.428]    [Pg.433]    [Pg.247]    [Pg.133]    [Pg.451]    [Pg.31]   
See also in sourсe #XX -- [ Pg.77 ]




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