Evaluating the photochemical reactivity of disinfection byproducts formed during seawater desalination processes

Leanne C Powers; Philippe Schmitt-Kopplin; Michael Gonsior

doi:10.1016/j.scitotenv.2023.169292

Evaluating the photochemical reactivity of disinfection byproducts formed during seawater desalination processes

Sci Total Environ. 2024 Feb 20:912:169292. doi: 10.1016/j.scitotenv.2023.169292. Epub 2023 Dec 15.

Authors

Leanne C Powers¹, Philippe Schmitt-Kopplin², Michael Gonsior³

Affiliations

¹ Department of Chemistry, State University of New York College of Environmental Science and Forestry, Syracuse, NY, United States. Electronic address: lcpowers@esf.edu.
² Helmholtz Munich, Research Unit Analytical BioGeoChemistry, Munich, Germany; Chair of Analytical Food Chemistry, Technical University München, Munich, Germany; Chesapeake Biological Laboratory, University of Maryland Center for Environmental Science, Solomons, MD, United States.
³ Chesapeake Biological Laboratory, University of Maryland Center for Environmental Science, Solomons, MD, United States.

PMID: 38104835
DOI: 10.1016/j.scitotenv.2023.169292

Abstract

Reverse osmosis (RO) is widely used for seawater desalination but pre-chlorination of intake water produces halogenated disinfection byproducts (DBPs). The fate and environmental impacts associated with the discharge of DBP-containing RO brine wastewater are unknown. Therefore, to evaluate if photochemistry plays a role in DBP degradation in seawater, we collected samples at a desalination plant, which were desalted and concentrated using two-inline solid phase extraction (SPE) techniques combining reverse-phase polymeric (PPL) and weak anion exchange (WAX) resins. Both filtered water samples and SPE samples (extracts reconstituted in open ocean seawater) were exposed to simulated sunlight in a custom-built flow-through system. Optical property analysis during irradiation experiments did not provide distinguishing features between intake water and RO reject water (brine). Extractable organic bromine (organoBr) concentrations were low in intake water samples (7.8 μg Br L^-1) and did not change significantly due to irradiation. OrganoBr concentrations in laboratory-chlorinated raw water were much higher (135 μg Br L^-1) and on average decreased by 42 % after 24 h irradiation. However, while organoBr concentrations were highest in RO reject water (473 μg Br L^-1), changes in organoBr concentrations in PPL SPE samples after 24 h irradiation were variable, ranging from a 1-46 % loss. Furthermore, most bromine-containing molecular ions identified by high resolution mass spectrometry that were present in RO reject water before irradiation were also found after both 24 h and 50 h exposures. Although only one RO reject water sample was tested in this study, results highlight that hundreds of yet to be identified brominated DBPs in RO reject water could be resistant to photodegradation or phototransform into existing DBPs in the environment. Future work examining the biolability of DBPs in RO reject water, as well as the interplay between photochemical and biological DBP cycling, is warranted.

Keywords: Desalination; Disinfection byproducts; Dissolved organic matter; FT-ICR MS; Photochemistry.