A groundwater arsenic plume, derived from arsenite wastes disposed at a chemical plant in Tacoma, WA, extends to the shore of the Hylebos Waterway. The plume is characterized by high-pH, high-silica concentrations generated by past disposal of high-pH brines on site. Aquifer K d values for arsenic decrease at least 10-fold as the pH increases from 8.5 to 11. Near the shore, aquifer sands are cemented, predominantly by opal quartz. Cementation reduces porosity to about 19%; however, very little pore space is interconnected. Along the shore face, a massive amorphous precipitate, high in Si and Mg, is found. SOLMINEQ calculations show that mixing high-pH, high-silica groundwater with seawater causes initial supersaturation of brucite [Mg(OH) 2 ] and magnesium hydroxysilicates. The cementation has likely considerably reduced the cumulative discharge of arsenic to the waterway.
No takes yet. Share an insight, caveat, or question.
Mariner et al. (1996) studied this question.
Synapse has enriched 2 closely related papers on similar clinical questions. Consider them for comparative context: