THESIS
2020
xxvii, 217 pages : illustrations (some color) ; 30 cm
Abstract
Seawater reverse osmosis (RO) desalination has been extensively applied to replenish
limited freshwater resources worldwide. However, disinfection byproducts (DBPs),
which potentially pose health, aesthetic and ecological risks, may be formed during the
disinfection step prior to RO. This study investigated DBP formation, fate, toxicity and
changes in seawater organic matter (SOM) during seawater RO desalination pretreated
with different disinfection strategies (i.e., chlorination, preformed chloramination, insitu
chloramination, and in-line chloramination) under various operating conditions (i.e., pH, contact time, oxidant dosage, and temperature).
Trihalomethanes (THMs), haloacetic acids (HAAs) and haloacetonitriles (HANs) were
the main DBP species formed in seawater chlor(am)...[
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Seawater reverse osmosis (RO) desalination has been extensively applied to replenish
limited freshwater resources worldwide. However, disinfection byproducts (DBPs),
which potentially pose health, aesthetic and ecological risks, may be formed during the
disinfection step prior to RO. This study investigated DBP formation, fate, toxicity and
changes in seawater organic matter (SOM) during seawater RO desalination pretreated
with different disinfection strategies (i.e., chlorination, preformed chloramination, insitu
chloramination, and in-line chloramination) under various operating conditions (i.e., pH, contact time, oxidant dosage, and temperature).
Trihalomethanes (THMs), haloacetic acids (HAAs) and haloacetonitriles (HANs) were
the main DBP species formed in seawater chlor(am)ination, and haloacetaldehydes
(HALs) were only detected in seawater chlorination. The concentrations of DBPs
formed under the baseline condition (pH = 8, contact time = 2 h, oxidant dosage = 2
mg/L as Cl
2, and temperature = 23°C) followed the order of chlorination > in-line
chloramination > in-situ chloramination > preformed chloramination. In general, the
concentrations of DBPs decreased with increasing pHs, but their concentrations
increased with longer contact times, higher oxidant dosages and higher temperatures.
The yield of unknown DBPs measured as high molecular weight (MW) adsorbable
organic halogen (AOX) in the preformed chloramination was higher than those in the
other strategies. In the preformed chloramination, relatively lower bromine substitution
factors (BSFs) and higher iodine substitution factors were observed, and they were
affected by pH, contact time and temperature. In contrast, BSFs of the detected DBPs
were always > 90% under various conditions in the other three strategies. The changes
in UV absorbance at 254 nm and fluorescence excitation-emission matrix volume were
strongly correlated with the concentrations of high MW AOX and total detected organic
halogen in the seawater chlorination, indicating that aromatic and humic fractions and
fluorophores in SOM were the primary precursors of these DBPs. The integrated cytoand
geno-toxicity in chlorination were always higher than that in chloramination and
preformed chloramination always gave the lowest, which was much lower than others.
Brominated HANs and HAAs were the main contributors of the integrated DBPinduced
cyto- and geno-toxicity in the four chlor(am)ination strategies, while HALs
also contributed significantly to the integrated cyto-toxicity in the seawater chlorination.
In the RO permeate pretreated by preformed chloramination, lower concentrations of
known DBPs but higher concentrations of high MW AOX were observed compared to
the other three strategies. The unknown chlorine- and bromine-containing DBPs in the RO permeates were characterized by Fourier transform ion cyclotron resonance mass
spectrometry. Highly saturated aliphatic DBPs (e.g., C
18H
35O
5Cl), which potentially
originated from fatty acids and their derivatives, were the most abundant DBPs in all
the strategies except preformed chloramination. The relative intensities of unknown
bromine-containing DBPs were significantly lower in the RO permeate pretreated by
chlorination compared to the other strategies. In the RO brine, the concentrations of
DBPs measured in the preformed chloramination were always significantly lower than
those detected in the other three pretreatment strategies. The trend of the experimentally
determined equivalent cytotoxicity correlated well with the concentrations of high MW
AOX in the three chloramination strategies, suggesting the importance of unknown
DBPs in the toxicity evaluation.
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