| Article ID | Journal | Published Year | Pages | File Type |
|---|---|---|---|---|
| 4429477 | Science of The Total Environment | 2012 | 8 Pages |
Soil-aquifer processes have proven to work as a natural treatment for the attenuation of numerous contaminants during artificial recharge of groundwater. Nowadays, significant scientific effort is being devoted to understanding the fate of pharmaceuticals in subsurface environments, and to verify if such semipersistent organic micropollutants could also be efficiently removed from water. In this context we carried out a series of batch experiments involving aquifer material, selected drugs (initial concentration of 1 μg/L and 1 mg/L), and denitrifying conditions. Diclofenac and sulfamethoxazole exhibited an unreported and peculiar behavior. Their concentrations consistently dropped in the middle of the tests but recovered toward the end, which suggest a complex effect of denitrifying conditions on aromatic amines. The transformation products Nitro-Diclofenac and 4-Nitro-Sulfamethoxazole were detected in the biotic experiments, while nitrite was present in the water. Their concentrations developed almost opposite to those of their respective parent compounds. We conjecture that this temporal and reversible effect of denitrifying conditions on the studied aromatic amines could have significant environmental implications, and could explain at least partially the wide range of removals in subsurface environments reported in literature for DCF and SMX, as well as some apparent discrepancies on SMX behavior.
► Fate of two aromatic amines in aquifer material, denitrifying conditions, batch tests. ► Diclofenac (DCF) and sulfamethoxazole (SMX) reversibly and temporarily affected. ► DCF&SMX concentrations: decrease as nitrite (NO2) builds up, rebound as NO2 disappear. ► Concurrently: nitro products formed in presence of NO2, being depleted as NO2 drops. ► Trend confirmed at 1 μg/L and 1 mg/L drugs' concentrations.
