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Immobilization of Nickel and Other Metals in Contaminated Sediments by Hydroxyapatite Addition

John C. Seaman, J.Samuel Arey and Paul M. Bertsch

Advanced Analytical Center for Environmental Sciences, Savannah River Ecology Lab., The Univ. of Georgia, Drawer E, Aiken, SC 29802



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Fig. 1. Effect of hydroxyapatite (HA) amendment on (A) Ni, (B) U (redrawn from Arey et al., 1999; Fig. 1), (C) PO4, and (D) pH for two sediments equilibrated in 0.02 M KCl or 0.01 M CaCl2.

 


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Fig. 2. Aqueous PO4 as related to (A) DOC concentration, (B) pH, and (C) Ni concentration in hydroxyapatite (HA)-amended sediments.

 


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Fig. 3. Effect of hydroxyapatite (HA) amendment on soluble (A) Ba, (B) Cd, (C) Co, and (D) Pb for two sediments equilibrated in 0.02 M KCl or 0.01 M CaCl2. Bars represent the standard deviation of the treatment means.

 


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Fig. 4. Effect of hydroxyapatite (HA) amendment on soluble (A) As and (B) Cr concentration for two sediments equilibrated in 0.02 M KCl or 0.01 M CaCl2. Bars represent the standard deviation of the treatment means.

 




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Fig. 5. Transmission electron microscope (TEM) micrographs of (A) fine-grained secondary Al/Fe-phosphate precipitates (40K magnification), (B) fine-grained, lath-shaped residual hydroxyapatite (HA) (50K magnification), and (C) typical energy dispersive x-ray (EDXA) spectrum of Ni- and U-rich secondary Al/Fe-phosphate precipitates in sediment S1 amended with 50 g kg-1 HA.

 


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Fig. 6. Toxicity Characteristic Leaching Procedure (TCLP) extractable Ni in HA-amended sediments (mg Ni kg-1 sediment). The TCLP values corrected for Ni extracted during initial equilibrations are included for comparison. Dashed line represents TCLP extractable Ni for nonamended sediments that were not subjected to the initial amendment equilibrations.

 


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Fig. 7. Nickel extracted in the Mn-occluded fraction for sediment (A) S1 and (B) S2 amended with various hydroxyapatite (HA) treatment levels and equilibrated in 0.02 M KCl or 0.01 M CaCl2.

 





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