Lignocellulosic bioreactors use solid-phase
substrates
such as
woodchips to sustain microbial respiration and have been applied to
treat agricultural runoff, stormwater, and other impaired waters.
Here, we query how respiration of different soluble electron acceptors
impacts the degradation of environmentally relevant pharmaceuticals
associated with treated municipal wastewater discharge. Laboratory-scale
columns containing a mixture of woodchips and alfalfa were manipulated
across nitrate- and sulfate-reducing conditions using residence time
and influent composition. Under steady-state conditions, bioreactors
dominated by nitrate reduction harbored a distinct phylogenetic profile
containing the genera Denitratisoma and increases
in the denitrification gene nirS. In contrast, bioreactors
where sulfate reduction dominated exhibited increased relative abundance
of fermenters (e.g., Obscuribacteriales) and putative sulfate reducers
(e.g., Desulfobulbus). Atenolol attenuation and biotransformation
to carboxy-metoprolol accelerated under nitrate-reducing conditions;
in contrast, trimethoprim attenuation and biotransformation to desmethyl
trimethoprim was nearly an order of magnitude faster under sulfate-reducing
conditions. Modest sulfamethoxazole attenuation occurred under all
tested conditions. Denitrification-associated rate constants for atenolol
were comparable to those reported in constructed wetlands and aquifer
recharge, suggesting commonality in biotransformation mechanisms.
Collectively, results suggest that manipulation of biogeochemical
gradients during nature-based treatment can be applied to attenuate
nitrate and trace quantities of pharmaceuticals.