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. Author manuscript; available in PMC: 2026 Jan 21.
Published in final edited form as: Environ Sci Technol. 2025 Jan 7;59(2):1421–1433. doi: 10.1021/acs.est.4c04255

Table 2:

Disinfection Byproducts (DBPs) and Total Organic Halogen Formed from the Treatment of MC-LRa

DBP chlorine chlorine + Cl UV/chlorine UV/chlorine + Cl no treatment
trichloromethane 1.7 1.4 ND 0.8 ND
trichloroacetaldehyde ND 0.9 0.9 0.9 ND
dichloroacetonitrile <0.75 <0.75 1.3 <0.75 ND
chloroacetonitrile 3.2 3.6 3.3 3.5 ND
1,1-dichloropropanone 1.0 <0.25 1.0 0.9 ND
chloropropanone 2.2 4.6 2.2 2.1 ND
trichloronitromethane 0.9 0.9 0.9 0.9 ND
dichloroacetamide 2.6 0.9 1.2 0.9 ND
trichloroacetamide 3.2 3.7 3.3 3.2 ND
chloroacetic acid 0.1 0.1 0.1 0.1 ND
dichloroacetic acid 0.5 0.4 0.1 0.3 ND
trichloroacetic acid <0.1 <0.1 <0.1 <0.1 ND
total DBPs 15.5 16.4 14.3 13.6 ND
TOC1 47.2 51.2 33.4 39.7 ND
TOBr ND ND ND ND ND
TOI ND ND ND ND ND
a

ND: not detected. DBPs that were not present in any of the sample sets are not listed. Results are the mean of 3 replicates. [FAC] = 1.5 mg/L, [Cl] = 5 mM, UV254 dose 70 mJ/cm2. TOC1 was detected in degradation experiments of MC-LR (1 mg/L) in four tested processes in pure water, with the following trend: Cl2 + Cl (51.2 μg/L) > Cl2 (47.2 μg/L) > UV/chlorine + Cl (39.7 μg/L) > UV/chlorine (33.4 μg/L). Thus, when integrating chlorine with UV, lower total concentrations of chlorinated DBPs (TOC1) were produced. No TOBr or TOI was detected (as expected), since bromide and iodide were not added to reactions.