Novel insights into the mechanisms for Sb mobilization in groundwater in a mining area: A colloid field study

Colloids may play an important role in the geochemical cycle of antimony (Sb). However, the controlling behaviors of colloids on Sb fate in contaminated groundwater are not available. To investigate the effects of colloids on Sb mobility, groundwater samples from Xikuangshan Sb Mine ' s two main aquifers (the D(3)s(2) aquifer and the D(3)x(4) aquifer) were successively (ultra)filtered through progressively decreasing pore sizes (0.45 mu m, 100 kDa, 50 kDa and 5 kDa). The results showed that 0.1-84.1% of Sb was adsorbed or carried by colloids, which corresponded to Sb concentration ranging between 0 and 2973 mu g/L in the colloids (0.45 mu m - 5 kDa). In both aquifers, Sb was closely associated with organic colloids (r = 0.72 p < 0.05 for the D(3)x(4) aquifer, r = 0.94 p < 0.01 for the D(3)s(2) aquifer). Parallel factor analysis of the three-dimensional fluorescence spectra determined that the proteinlike substances in the D(3)x(4) aquifer and the humus-like substances in the D(3)s(2) aquifer controlled Sb behavior. Xray absorption spectroscopy confirmed Sb complexing with organic substances. Competitive adsorption of As and Sb suppressed the complexation of colloids with Sb, particularly in the D(3)x(4) aquifer (r = -0.71, p < 0.05). Sb mobility was also influenced by the redox of the groundwater system. As the oxidation-reduction potential and dissolved oxygen increased, Sb in the colloidal fractions decreased. These findings provide new insights into the mechanisms involved in Sb fate affected by colloids, establishing the theoretical basis for developing effective Sb and even metalloid pollution remediation strategies.

Automated summary

Colloids play an important role in the geochemical cycle of antimony (Sb) and have a significant impact on Sb mobility in contaminated groundwater. Organic colloids were found to closely associate with Sb, and the behavior of Sb was controlled by proteinlike substances and humus-like substances. Competitive adsorption of arsenic (As) and Sb suppressed the complexation of colloids with Sb, and the redox of the groundwater system also influenced Sb mobility. These findings provide new insights into the mechanisms involved in Sb fate affected by colloids and offer a theoretical basis for developing effective Sb and metalloid pollution remediation strategies.