Widespread
application of neonicotinoids has led to their proliferation
in waters. Despite low neonicotinoid hydrophobicity, our prior studies
implicated granular activated carbon (GAC) in neonicotinoid removal.
Based on known receptor binding characteristics, we hypothesized that
the insecticidal pharmacophore influences neonicotinoid sorption.
Our objectives were to illuminate drivers of neonicotinoid sorption
for parent neonicotinoids (imidacloprid, clothianidin, thiamethoxam,
and thiacloprid) and pharmacophore-altered metabolites (desnitro-imidacloprid
and imidacloprid urea) to GAC, powdered activated carbon, and carbon
nanotubes (CNTs). Neonicotinoid sorption to GAC was extensive and
largely irreversible, with significantly greater sorption of imidacloprid
than desnitro-imidacloprid. Imidacloprid and imidacloprid urea (electronegative
pharmacophores) sorbed most extensively to nonfunctionalized CNTs,
whereas desnitro-imidacloprid (positive pharmacophore) sorbed most
to COOH-CNTs, indicating the importance of charge interactions and/or
hydrogen bonding between the pharmacophore and carbon surface. Water
chemistry parameters (temperature, alkalinity, ionic strength, and
humic acid) inhibited overall neonicotinoid sorption, suggesting that
pharmacophore-driven sorption in real waters may be diminished. Analysis
of a full-scale drinking water treatment plant GAC filter influent,
effluent, and spent GAC attributes neonicotinoid/metabolite removal
to GAC under real-world conditions for the first time. Our results
demonstrate that the neonicotinoid pharmacophore not only confers
insecticide selectivity but also impacts sorption behavior, leading
to less effective removal of metabolites by GAC filters in water treatment.