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Reduction of Heavy Metals

Industrial and municipal waste incinerators often emit heavy metals (e.g., Cd, Hg, Tl, Sb, As, Pb, Cr, Co, Cu, Mn, Ni, V and Sn) arising from items such as batteries, inks, pigments, plated metal and circuit boards. Many of the metals vaporise at the temperatures of 930 to 1200 °C required to destroy toxic organic compounds, but those with higher boiling points generally form sufficiently large particles when cooled to be removed in dust collectors to less than 1 mg/Nm [29.12]. [Pg.342]

Mercury and cadmium are more volatile (boiling points 356 and 765 °C respectively) and are consequently more difficult to remove. They are reduced to about 0.2mg/Nm in total in the semi-dry scrubbing and pre-cooled dry injection processes and to about 0.1 mg/Nm in the wet scrubbing processes [29.10]. Where lower emission levels are required, the injection of activated carbon can reduce the level to 0.05 mg/Nm [29.10]. [Pg.342]


Charging and tapping emissions are controlled by a variety of evacuation systems and operating practices. Charging hoods, tapside enclosures, and full furnace enclosures are used in the industry to capture these emissions and send them to either the primary hood gas cleaner or a second gas cleaner.1516 Pollution prevention opportunities for the reduction of heavy metals at the BOF are limited as heavy metals are an inherent part of the iron ore material stream, so the higher the iron production, the greater will be the use of the ore. [Pg.52]

Chemical precipitation is used in porcelain enameling to precipitate dissolved metals and phosphates. Chemical precipitation can be utilized to permit removal of metal ions such as iron, lead, tin, copper, zinc, cadmium, aluminum, mercury, manganese, cobalt, antimony, arsenic, beryllium, molybdenum, and trivalent chromium. Removal efficiency can approach 100% for the reduction of heavy metal ions. Porcelain enameling plants commonly use lime, caustic, and carbonate for chemical precipitation and pH adjustment. Coagulants used in the industry include alum, ferric chloride, ferric sulfate, and polymers.10-12... [Pg.329]

Schumacher U. (2005). Reduction of heavy metal input - a task also for organic animal husbandry , in, Hovi M., Zastawny J. and Padel S. Proceeding of the 3rd SAFO Workshop, 16-18 September 2004, Falenty, Poland. University of Reading, 91-92. [Pg.142]

The present reevaluation of the monitoring time series is aimed at assessing whether the reduction of heavy metal discharges entering the Baltic have had a measurable effect on heavy metal concentrations in the Baltic Sea environment. The natural geochemical... [Pg.372]

Oxidation-Reduction of Heavy Metal Turnings. Heavy metal turnings can be easily oxidized by air at about 800 °C. The layer height in this step is critical, because if it exceeds a certain limit then local overheating (exothermic reaction) can cause melting. The oxidized product is subsequently milled and screened and, finally, it is reduced in hydrogen atmosphere at 900-1000 °C in the same type of push-t5q)e furnaces used for W-powder production. [Pg.384]

Tab. 9.2 Specific reduction of heavy metals from household waste by separate collection (reference value 230 kg per person per year). (From Bilitewski et al. 1997)... Tab. 9.2 Specific reduction of heavy metals from household waste by separate collection (reference value 230 kg per person per year). (From Bilitewski et al. 1997)...
In Austria, in the last couple of years first steps have been set to the reduction of heavy metal emissions. These were specific measures such as the prohibition of leaded gasoline from 1993, but also non-specific measures for the reduction of particulate emissions in industry and power plants which simultaneously brought about a reduction in heavy metal emissions. Nevertheless, further measures for the reduction of heavy metal emissions are considered to be necessary due to their higher local incidence. Generally, lead represents the most important heavy metal emitted in Austria (Table 4) (Federal Ministry for Environment, Youth and Family, 1997). [Pg.116]

Viarengo, A., Bettella, E., Fabbri, R., Burlando, B., Lafaurie, M., 1997. Heavy metal inhibition of EROD activity in liver microsomes from the bass Dicentrarchus labrax exposed to organic xenobiotics role of GSH in the reduction of heavy metal effects. Mar. Environ. Res. 44, 1-11. [Pg.454]

Several new isocyanide complexes of chromium(m) have been prepared by the electrochemical reduction of heavy-metal adducts of chromium(iii) aquocyano-complexes, and characterized by their visible spectra. The chromium 2p- and 3s-orbital ionization potentials in K3[Cr(NCS)6] have been reported, and the lattice parameters for this anion in the salt with diaquotris-(nicotinic acid)holmium(iii) determined. " The absorption spectra of the... [Pg.109]

The non-biodegradable water soluble heavy metals are either oxidized or reduced by the microorganisms and produce less soluble species. The less soluble form of these metals which are formed due to microbial reactions are adsorbed or precipitated/co-precipitated on the surface of the adsorbent and the extra cellular protein of the microorganisms in the biolayer (Srivastava and Majumder, 2008 Vails and Lorenzo, 2002). The methylation of metals is also another important route for bioremediation of heavy metals in water (White et al, 1997). Though the microbial action on metal ion transformation is still a matter of research, it is assumed that there are two paths. In one path oxidation or reduction of heavy metal ions takes place by extra cellular enzymes where the metal ions do not enter into the bacterial cell. In the other path the metal ions are transported into the microbial cells by trans-membrane proteins and are converted to other less soluble forms by metabolic actions of enzymes in the cells followed by subsequent excretion from the cells, yet both the paths are plasmid mediated (Vails and Lorenzo, 2002). Whether the microbial action on a metal ion is performed by only one path or by both the paths is a matter of research. [Pg.180]

A detailed analysis of the plastic addition in the combustor of municipal waste has proven their positive effect. The ash quality was improved through further reduction of heavy metals content and the polychlorinated dioxines amount was not increased even for a 8-10 wt% PVC content [434]. [Pg.464]


See other pages where Reduction of Heavy Metals is mentioned: [Pg.2227]    [Pg.22]    [Pg.420]    [Pg.523]    [Pg.15]    [Pg.77]    [Pg.66]    [Pg.3883]    [Pg.25]    [Pg.74]    [Pg.2470]    [Pg.3]    [Pg.307]    [Pg.329]    [Pg.274]    [Pg.2451]    [Pg.6]    [Pg.75]    [Pg.253]    [Pg.342]    [Pg.2231]    [Pg.73]   


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