Ozonation
is widely used in wastewater reclamation treatment trains,
either for micropollutant control or as a disinfectant and preoxidant
in certain reuse processes. We recently found that ozonation of secondary
effluent produces nitromethane, which can be efficiently transformed
to genotoxic halonitromethanes by chlorination. In this work, the
fate of nitromethane through water reuse treatment trains was characterized
by analyzing samples from five reuse operations employing ozone. Nitromethane
was poorly (<50%) rejected by reserve osmosis (RO), not removed
by, and in some cases, increased by ultraviolet/advanced oxidation
processes (UV/AOP). Sufficient nitromethane remained after advanced
treatment that when chlorine was added to mimic secondary disinfection,
halonitromethane formation was consistently observed. In contrast,
biological activated carbon removed most (>75%) nitromethane. Bench-scale
experiments were conducted to verify low removal by RO in clean systems
and with wastewater effluent and to quantify the kinetics of direct
and indirect photolysis of nitromethane in UV/AOP. An explanation
for increasing nitromethane concentration during AOP is proposed.
These results indicate that nitromethane presents a unique hazard
to direct potable reuse systems, due to its ubiquitous formation during
wastewater ozonation, poor removal by RO and UV/AOP, and facile conversion
into genotoxic halonitromethanes upon chlorine addition.