INVESTIGATING ARSENIC MINERALOGY IN HISTORIC MINE WASTE FROM THE IDAHO-MARYLAND MINE (GRASS VALLEY, CALIFORNIA) USING SEM-EDS
A TeScan© VEGA-3 SEM (25 kV, beam intensity 15) with 2 Oxford© EDS detectors was used to image and chemically map large areas (<134 mm2 @ 200x mag). We analyzed single-element maps, phase maps, and spectra collected from individual As-bearing grains.
Our analysis identified ~10 unique As-bearing phases. Two commonly occurring, high-As (>20 to ~44 wt% As) phases had low modal abundance: arsenopyrite (FeAsS; 47% of samples) and As-Fe oxide (20% of samples)—these phases never co-occur in any samples. FeAsS grains always had micrometers-thick weathering rinds containing As. Phases with low levels of As (<1 wt%) were most common (60% of samples, representing >99% of As-bearing pixels); Fe co-occurred in all As-bearing phases. SEM-EDS did not detect As in pyrite (ideal formula: FeS2; detection limit of ~0.3 wt%), although pyrite can contain several wt% As (Foster & Kim, 2014. Rev. Min. Geochem. v. 79. pp. 257-369).
Arsenic bioaccessibility measurements can be influenced by rare, highly bioaccessible phases and/or common, low bioaccessibility phases. Our analytical approach allows us to evaluate arsenic mineral residence on a sample by sample basis. We will complement these analyses with microRaman and EMPA data and compare with As bioaccessibility measurements from the same samples. SEM-EDS automated mapping can be a valuable tool to characterize the mineral residence of trace elements of concern, and to improve understanding of human-health risk based on mineralogy.