NATO/CCMS Pilot Study Evaluation of Demonstrated and ... - CLU-IN
NATO/CCMS Pilot Study Evaluation of Demonstrated and ... - CLU-IN
NATO/CCMS Pilot Study Evaluation of Demonstrated and ... - CLU-IN
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<strong>NATO</strong>/<strong>CCMS</strong> <strong>Pilot</strong> Project on Contaminated L<strong>and</strong> <strong>and</strong> Groundwater (Phase III) January 2001<br />
6. HEALTH AND SAFETY<br />
The primary components <strong>of</strong> the unconventional sorbent suspensions, i.e., red muds <strong>and</strong> fly ashes<br />
containing Fe2O3, Al2O3, SiO2, TiO2 <strong>and</strong> some aluminosilicates, to be used as barrier material are<br />
essentially non-toxic. The tested heavy metals, either as free ions or in chelated forms, i.e., Cd 2+ , Pb 2+<br />
(<strong>and</strong> partly Cu 2+ ) <strong>and</strong> Cd-EDTA 2− , Pb-EDTA 2− , Cu-EDTA 2− , were toxic, so care should be exercised<br />
especially in solidification/ stabilization processes using the heavy metal-loaded sorbents in dry form<br />
where small particles could be inhaled by workers. Also working with radionuclide solutions, even in<br />
very dilute forms, needs special pipettes <strong>and</strong> glassware to be used under a hood on a stainless steel<br />
workbench, <strong>and</strong> special laboratory practice with workers wearing radiation dosimeters. All waste<br />
solutions, even at very low-level activity, should be properly collected <strong>and</strong> submitted to the nuclear<br />
energy authority for waste storage <strong>and</strong> stabilization.<br />
7. ENVIRONMENTAL IMPACTS<br />
Prior acid or water leaching <strong>of</strong> the sorbents before adsorption experiments did not effectively increase the<br />
specific surface area or chemical adsorption power <strong>of</strong> these sorbents, but rather these sorbents were<br />
stabilized so as not to leach out any micropollutants to water at the time <strong>of</strong> heavy metal adsorption. It is<br />
also indicated in literature that iron oxyhydroxide based grouts as barrier material can be made from low<br />
cost industrial by-products, which should be tested for safety <strong>and</strong> effectiveness on a case-by-case basis<br />
(Hapka et al., 1995). Thus these criteria should be judged for red muds <strong>and</strong> fly ashes.<br />
Stabilization/solidification <strong>of</strong> the metal-loaded solid wastes puts these wastes <strong>and</strong> incorporated toxic<br />
metals into environmentally safe (mechanically strong, durable <strong>and</strong> unleachable) forms. The matrix<br />
disrupting effect <strong>of</strong> Pb was eliminated by using relatively small amounts <strong>of</strong> sodium aluminate or calcium<br />
phosphate to improve the setting, hardening <strong>and</strong> mechanical properties <strong>of</strong> the final concrete blocks. It was<br />
environmentally safe to observe that the matrix-held metals (either as a result <strong>of</strong> irreversible adsorption or<br />
solidification) did not leach out by carbonate or carbonic acid solutions ensuring the chemical stability <strong>of</strong><br />
these solid wastes under changing groundwater conditions.<br />
8. COSTS<br />
Because iron-based grouts (without relatively expensive additives such as citric acid, urea, <strong>and</strong> urease)<br />
can be prepared from inexpensive by-products, the primary costs involved come from transportation <strong>and</strong><br />
additives (Jet grouted, 25% grout) roughly around 50 USD per m 2 for 1m thick wall, i.e., or 50 USD for 1<br />
cubic meter. The overall cost data have not yet been obtained.<br />
9. CON<strong>CLU</strong>SIONS<br />
In investigation <strong>of</strong> the possibility <strong>of</strong> usage <strong>of</strong> metallurgical solid wastes as cost-effective sorbents in<br />
heavy metal (Pb, Cu, Cd) <strong>and</strong> radionuclide (Cs-137 <strong>and</strong> Sr-90) removal from contaminated water, red<br />
muds <strong>and</strong> especially fly ashes have been shown to exhibit a high capacity. Extensive modeling <strong>of</strong> heavy<br />
metal sorption—either as free metal ions or in the form <strong>of</strong> EDTA-chelates—has been performed by<br />
simple quadratic equations in terms <strong>of</strong> the retained metal concentration in the sorbent phase. These<br />
modeling efforts enable the prediction <strong>of</strong> heavy metal adsorption in different media over a wide pH <strong>and</strong><br />
concentration range. The developed iron- <strong>and</strong> aluminum-oxide based sorbents may be used as barrier<br />
material as cost-effective grout for the prevention <strong>of</strong> expansion <strong>of</strong> a heavy metal contaminant plume.<br />
Heavy metal-loaded solid wastes have been effectively solidified by adding cement, s<strong>and</strong>, <strong>and</strong> water. The<br />
setting <strong>and</strong> mechanical properties <strong>of</strong> concrete specimens obtained by optimal dosage <strong>of</strong> waste addition<br />
were satisfactory. The fixed heavy metals did not leach out appreciably into water over extended periods.<br />
The usage <strong>of</strong> iron fillings as potential barrier material has been successfully tested for the management <strong>of</strong><br />
textile dyeing wastes, i.e., acid blue <strong>and</strong> acid yellow.<br />
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