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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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techniques can be useful in a study <strong>of</strong> metal uptake in plants, where transfer takes place<br />

predominately via a solution phase. However, one must keep in mind that they are not<br />

“selective” in metal species, give no particle size in<strong>for</strong>mation and, above all, these leachable<br />

fractions have never been correlated to bioavailability.<br />

Solution Speciation Using Computer-Based Models. Computer-based models are either<br />

based upon equilibrium constants or upon Gibb’s free energy values in determining metal<br />

speciation from solution chemistry conditions (concentration, pH, Eh, organic complexes,<br />

adsorption/desorption sites, and temperature). Both approaches are subject to mass balance and<br />

equilibrium conditions. These models have undergone a great deal <strong>of</strong> development in recent<br />

years, as reliable thermodynamic data has become available and can provide some predictive<br />

estimates <strong>of</strong> metal behavior. A good review <strong>of</strong> these models and their applications is provided<br />

by Lumsdon and Evans (1995).<br />

Speciation can be controlled by simple reactions; however, in many cases, particularly in<br />

contaminated media, their state <strong>of</strong> equilibrium and reversibility are unknown. In addition, these<br />

models suffer from other limitations such as a lack <strong>of</strong> reliable thermodynamic data on relevant<br />

species, inadequacies in models to correct <strong>for</strong> high ionic strength, reaction kinetics are poorly<br />

known, and complex reactions with co-precipitation/adsorption are not modeled.<br />

The first limitation is perhaps the most significant <strong>for</strong> contaminated media. For example,<br />

none <strong>of</strong> the models would predict the common, anthropogenic, Pb phases, i.e., paint, solder,<br />

and slag.<br />

AX7.1.1.4 Biotic Ligand Model<br />

The biotic ligand model (BLM) is an equilibrium-based conceptual model that has been<br />

incorporated into regulatory agencies guidelines (including the <strong>EPA</strong>) to predict effects <strong>of</strong> metals<br />

primarily on aquatic biota and to aid in the understanding <strong>of</strong> their interactions with biological<br />

surfaces (see Annex Section AX7.2.1.3).<br />

Because <strong>of</strong> assumed similarities in mechanisms <strong>of</strong> toxicity between aquatic and terrestrial<br />

organisms, it is likely that the BLM approach as developed <strong>for</strong> the aquatic compartment may also<br />

be applicable to the terrestrial environment. Recent research has been directed toward extending<br />

the BLM to predict metal toxicity in soils (Steenbergen et al., 2005). Steenbergen et al. (2005)<br />

pointed out that, until recently, the BLM concept has not been applied to predict toxicity to soil<br />

AX7-18

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