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Heavy metals associated with

In this work, atmospheric particles (PM 10 and PM 2.5) were collected by a dichotomos air sampler. Several leaching procedures were investigated for decomposition of heavy metals. The digests were pre-concentrated with sodium diethyldithiocarbamate. The determinations were canted out on a Vartan Model AA-220 atomic absorption spectrometer. The instrarment was equipped with a GTA-110 graphite furnace system. Table 1 shows the concentrations of heavy metals associated with PM 10 and PM 2.5 particles. Table 1. Concentrations of heavy metals in PM 10 and PM 2.5 atmospheric particles (ng/m )... [Pg.237]

Campbell, K.R. 1994. Concentrations of heavy metals associated with urban runoff in fish living in stormwater treatment ponds. Arch. Environ. Contam. Toxicol. 27 352-356. [Pg.520]

Exner, A.,Theisen, M., Panne, U., and Niessner, R. (2000). Combination of asymmetric flow field-flow fractionation (AF4) and total-reflexion X-ray fluorescence analysis (TXRF) for determination of heavy metals associated with colloidal humic substances. Fresenius J. Anal. Chem. 366, 254-259. [Pg.397]

Road dust and run-off. Roads are a potentially important source of environmental contamination. Concerns include NO, PAHs and organo-lead from exhaust emission, and a variety of heavy metals associated with vehicle manufacture and use. [Pg.284]

Tillekeratne, S., Hiraide, M. and Mizuike, A. (1984) Selective leaching of trace heavy metals associated with suspended matter in fresh waters. Mkrochim. Acta, 1984 III, 69. [Pg.321]

To Filter or Not to Filter Many homes use water filters to purify tap water. These students lived either at home or in off-campus housing. Since the homes were older, the students were interested in the effectiveness of standard, readily available water filters and in the ability of filters to remove heavy metals associated with pipes in older homes. The students designed experiments to test water for lead and copper and evaluated how effective household water filters were in removing such metal ions. The students also investigated types of home filters and the methods of filtration. [Pg.39]

The impact to health has been mostly dependent on the concentration of the candidate metal. Some metals (e.g., mercury, lead, arsenic, cadmium, iron, copper) ultimately find their way into human systems via soil, minerals, and water. Studies have shown the presence of many metals in daily consumable products (e.g., food, fruits, milk, fabric materials, drinking water). Further, heavy metals associated with particle material can be accumulated in areas suitable for sedimentation or particle concentration (e.g., upstream from sills or dams, in estuary sludge clog, etc.). These accumulation areas are creating possible pollution sources, as particles pooled could be resuspended during punctual hydrologic periods (floods, drains). Bioavailability, and therefore toxicity of heavy metals, is strongly bound to the current chemical form. [Pg.61]

J. L. Uhrie, J. I. Drever, P. J. S. Colberg, and C. C. Nesbitt, In Situ Immobilization of Heavy Metals Associated with Uranium Leach Mines by Bacterial Sulfate Reduction, Hydrometallurgy, 43 231-239 (1996). [Pg.58]

Figure 3. Relative concentrations of heavy metals associated with major carrier phases mgjkg metal vs. mgjkg carrier phase (ordinate absolute... Figure 3. Relative concentrations of heavy metals associated with major carrier phases mgjkg metal vs. mgjkg carrier phase (ordinate absolute...
Particulate matter may physically become a factor in leaf physiological function if deposition is heavy enough to block light (critical to the photosynthetic machinery of the leaf) or if stomata become occluded by the particles. In the latter case both uptake of carbon dioxide for photosynthesis and water loss by the plant could be reduced. Particulate matter also has a potential to chemically alter the micro-environment of the leaf surface. Trace concentrations of heavy metals associated with deposited particles, as well as strong acid anions, may significantly modify the chemical nature of water drops or films of water in contact with plant surfaces. [Pg.261]

Combination of more exnaction instfuments, that is, their successive use on the same sample, had first been applied by Gibbs [81], in the course of examination of suspended river material, and afterwards this method, with various modifications and improvements, was used by a number of authors, amongst whom probably the best known are Tessier [82, 83] and Foersmer [84-87], Very quickly the authors adopted the division into phases, which logically ensues from chemical characteristics of applicable extraction instruments, in other words, extraction instruments which meet the criteria of efficiency and selectivity to the maximum. Under phases here are implied discrete physical phases of geological material (i.e. silicate, oxide, carbonate, sulphide, organic phase, as well as fractions of heavy metals associated with them) whilst in the case of non-selectively bound metals an expression sorptive or exchangeable phase. [Pg.290]

From Figure 10 it is evident that there are good correlations between Mn and Mg extracted after the first phase of sequential extraction (most soluble fraction) and Mg extracted after the second phase. These results indicate binding of soluble Mn and Mg with magnesium in the form of Mg-carbonates. These correlations are in corroboration with another section of Fig. 10, the correlation between Mn and Mg, both extracted after the second phase. This correlation indicates interactions between Mg-carbonates and Mn-hydroxides, the two main substrates for heavy metals in river sediment samples. This means that a slight decrease of pH value and ionic strength will release heavy metals associated with both Mg-carbonate and Mn-hydroxide substrates. [Pg.312]

Giannissis, D., G. Dorange, and M. Guy, (1985), Association (Complexation and Adsorption) Phenomena of Heavy Metal Cations with Humic Substances (Role of Calcium Ions), in T. D. Lekkas, Ed., 5th International Conference on Heavy Metals in the Environment, Vol. 2, pp. 469-471. [Pg.169]

Just over 20% of the electricity generated in the United States is produced by nuclear power plants. In 1995, 32,200 metric tons of spent fuel, with a total activity of 30,200 MCi, was stored by the electric utilities at 70 sites (either in pools or in dry storage systems) (Ahearne 1997, Richardson 1997). By 2020, the projected inventory will be 77,100 metric tons of heavy metal (MTHM) with a total activity of 34,600 MCi. Although the volume of the spent fuel is only a few percent of the volume of HLW, over 95% of the total activity (defense-related plus commercially generated waste) is associated with the commercially generated spent nuclear fuel (Crowley 1997). At present in the United States, none of the spent fuel will be reprocessed all is destined for direct disposal in a geological repository at Yucca Mountain, Nevada (Hanks et al. 1999). [Pg.674]

The type of substrate the metal is bound to, determines its propensity to be mobilized under completely specific conditions - the metal co-precipitated with carbonates can reach the water environment due to the decrease of a pH, while ions sorbated onto hydrous ferric oxides will be mobilized if there is a decrease in the redox potential, etc. On the other hand, the strength of the connection which the ion of a heavy metal establishes with its substrate will directly determine its mobility - the ion bound by weak, adsorptive connections to some substrate will easily convert into a solution, while the huminous associated metals will be firmly bound to... [Pg.288]

Marine organisms tend to concentrate heavy metals, particularly shellfish, but lead has substantially lower concentration factors than other metals at 2600 1 compared with 32 500 for zinc, 10 500 for copper and 4500 for cadntium. There are often greater concerns for environmental contantination from other metals associated with lead smelting such as arsenic, antimony, cadntium, selenium and thallium. [Pg.249]

Hafnium [7440-58-6] Hf, is in Group 4 (IVB) of the Periodic Table as are the lighter elements zirconium and titanium. Hafnium is a heavy gray-white metallic element never found free in nature. It is always found associated with the more plentiful zirconium. The two elements are almost identical in chemical behavior. This close similarity in chemical properties is related to the configuration of the valence electrons, and for zirconium and... [Pg.439]


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