7 research outputs found
Toxicity of Drinking Water Disinfection Byproducts: Cell Cycle Alterations Induced by the Monohaloacetonitriles
Haloacetonitriles
(HANs) are a chemical class of drinking water
disinfection byproducts (DBPs) that form from reactions between disinfectants
and nitrogen-containing precursors, the latter more prevalent in water
sources impacted by algae bloom and municipal wastewater effluent
discharge. HANs, previously demonstrated to be genotoxic, were investigated
for their effects on the mammalian cell cycle. Treating Chinese hamster
ovary (CHO) cells with monoHANs followed by the release from the chemical
treatment resulted in the accumulation of abnormally high DNA content
in cells over time (hyperploid). The potency for the cell cycle alteration
followed the order: iodoacetonitrile (IAN) > bromoacetonitrile
(BAN)
≫ chloroacetonitrile (CAN). Exposure to 6 μM IAN, 12
μM BAN and 900 μM CAN after 26 h post-treatment incubation
resulted in DNA repair; however, subsequent cell cycle alteration
effects were observed. Cell proliferation of HAN-treated cells was
suppressed for as long as 43 to 52 h. Enlarged cell size was observed
after 52 h post-treatment incubation without the induction of cytotoxicity.
The HAN-mediated cell cycle alteration was mitosis- and proliferation-dependent,
which suggests that HAN treatment induced mitosis override, and that
HAN-treated cells proceeded into S phase and directly into the next
cell cycle. Cells with multiples genomes would result in aneuploidy
(state of abnormal chromosome number and DNA content) at the next
mitosis since extra centrosomes could compromise the assembly of bipolar
spindles. There is accumulating evidence of a transient tetraploid
state proceeding to aneuploidy in cancer progression. Biological self-defense
systems to ensure genomic stability and to eliminate tetraploid cells
exist in eukaryotic cells. A key tumor suppressor gene, p53, is oftentimes
mutated in various types of human cancer. It is possible that HAN
disruption of the normal cell cycle and the generation of aberrant
cells with an abnormal number of chromosomes may contribute to cancer
induction and perhaps be involved in the induction of adverse pregnancy
outcomes associated with long-term consumption of disinfected water.
Here we present the first observation of the induction of hyperploidy
by a class of DBPs
Butyrate Enhances γ‑H2AX Induced by Benzo[<i>a</i>]pyrene
Benzo[a]pyrene (BaP) is known to form
DNA adduct
following metabolic activation, which causes phosphorylation of histone
H2AX (γ-H2AX). Recent studies have shown that histone deacetylase
(HDAC) inhibitors enhanced BaP-induced CYP1A1 gene
expression. In this study, we examined the relationship between the
HDAC inhibitor-augmented metabolic activation and BaP-induced γ-H2AX.
Sodium butyrate (SB), a typical HDAC inhibitor, enhanced BaP-induced
γ-H2AX. The enhanced DNA damage was further confirmed by biased
sinusoidal field gel electrophoresis, which detects DNA double-strand
breaks. SB remarkably augmented BaP-induced CYP1A1 gene expression, and CYP1A1-overexpressing cells
showed elevated generation of γ-H2AX. Furthermore, SB enhanced
intracellular oxidation after treatment with BaP. These results suggested
that SB-induced CYP1A1 upregulation facilitated BaP metabolism, which
might result in excess DNA adducts or oxidative DNA damages, leading
to augmentation of γ-H2AX
Chloroacetonitrile and <i>N</i>,2-Dichloroacetamide Formation from the Reaction of Chloroacetaldehyde and Monochloramine in Water
Combined chlorine is increasingly
being used as an alternative
disinfectant to free chlorine to maintain a residual in drinking water
distribution systems mainly because it would reduce the formation
of regulated disinfection byproducts (DBPs) trihalomethanes and haloacetic
acids. However, the use of combined chlorine could promote the formation
of currently unregulated nitrogenous DBPs (N-DBPs) such as haloacetonitriles
and haloacetamides that are found to be more cyto- and genotoxic than
regulated DBPs. Monochloramine quickly reacts with chloroacetaldehyde,
a DBP formed during primary disinfection with free chlorine, forming
and reaching pseudoequilibrium (equilibrium constant <i>K</i><sub>1</sub> = 1.87 × 10<sup>3</sup> M<sup>–1</sup>)
with the carbinolamine 2-chloro-1-(chloroamino)Âethanol. 2-Chloro-1-(chloroamino)Âethanol
undergoes slow dehydration to form the imine 1-chloro-2-(chloroimino)Âethane
that decomposes at a faster rate to chloroacetonitrile. 2-Chloro-1-(chloroamino)Âethanol
is also oxidized by monochloramine to produce the previously unreported
DBP <i>N</i>,2-dichloroacetamide. The carbinolamine dehydration
step was found to be acid/base catalyzed (<i>k</i><sub>2</sub><sup>0</sup> = 3.30 × 10<sup>–6</sup> s<sup>–1</sup>, <i>k</i><sub>2</sub><sup>H</sup> = 2.43 M<sup>–1</sup> s<sup>–1</sup>, <i>k</i><sub>2</sub><sup>OH</sup> = 3.90 M<sup>–1</sup> s<sup>–1</sup>). In contrast, <i>N</i>,2-dichloroacetamide formation was observed to be only
base catalyzed (<i>k</i><sub>3</sub><sup>OH</sup> = 3.03
× 10<sup>4</sup> M<sup>–2</sup> s<sup>–1</sup>). <i>N</i>,2-dichloroacetamide cytotoxicity (LC<sub>50</sub> = 2.56
× 10<sup>–4</sup> M) was found to be slightly lower compared
to that reported for chloroacetamide but higher than those of di-
and trichloroacetamide
Acetonitrile and <i>N</i>‑Chloroacetamide Formation from the Reaction of Acetaldehyde and Monochloramine
Nitriles and amides
are two classes of nitrogenous disinfection
byproducts (DBPs) associated with chloramination that are more cytotoxic
and genotoxic than regulated DBPs. Monochloramine reacts with acetaldehyde,
a common ozone and free chlorine disinfection byproduct, to form 1-(chloroamino)Âethanol.
Equilibrium (<i>K</i><sub>1</sub>) and forward and reverse
rate (<i>k</i><sub>1</sub>,<i>k</i><sub>–1</sub>) constants for the reaction between initial reactants and 1-(chloroamino)Âethanol
were determined between 2 and 30 °C. Activation energies for <i>k</i><sub>1</sub> and <i>k</i><sub>–1</sub> were 3.04 and 45.2 kJ·mol<sup>–1</sup>, respectively,
and enthalpy change for <i>K</i><sub>1</sub> was −42.1
kJ·mol<sup>–1</sup>. In parallel reactions, 1-(chloroamino)Âethanol
(1) slowly dehydrated (<i>k</i><sub>2</sub>) to (chloroimino)Âethane
that further decomposed to acetonitrile and (2) was oxidized (<i>k</i><sub>3</sub>) by monochloramine to produce <i>N</i>-chloroacetamide. Both reactions were acid/base catalyzed, and rate
constants were characterized at 10, 18, and 25 °C. Modeling for
drinking water distribution system conditions showed that <i>N</i>-chloroacetamide and acetonitrile concentrations were 5–9
times higher at pH 9.0 compared to 7.8. Furthermore, acetonitrile
concentration was found to form 7–10 times higher than <i>N</i>-chloroacetamide under typical monochloramine and acetaldehyde
concentrations. <i>N</i>-chloroacetamide cytotoxicity (LC<sub>50</sub> = 1.78 × 10<sup>–3</sup> M) was comparable to
dichloroacetamide and trichloroacetamide, but less potent than <i>N</i>,2-dichloroacetamide and chloroacetamide. While <i>N</i>-chloroacetamide was not found to be genotoxic, <i>N</i>,2-dichloroacetamide genotoxic potency (5.19 × 10<sup>–3</sup> M) was on the same order of magnitude as chloroacetamide
and trichloroacetamide
Chlorotyrosines versus Volatile Byproducts from Chlorine Disinfection during Washing of Spinach and Lettuce
Following
the Food Safety Modernization Act of 2011 in the U.S.,
guidelines for disinfection washes in food packaging facilities are
under consideration to control pathogen risks. However, disinfectant
exposures may need optimization because the high concentrations of
chlorine disinfectant promote the formation of high levels of disinfection
byproducts (DBPs). When chlorine doses up through the 200 mg/L as
Cl<sub>2</sub> range relevant to the current practice were applied
to spinach and lettuce, significant DBP formation was observed, even
within 5 min at 7 °C. Concentrations of volatile chlorinated
DBPs in washwater were far higher than typically observed in disinfected
drinking water (e.g., 350 μg/L 1,1-dichloropropanone). However,
these DBPs partitioned to the aqueous phase and so represent a greater
concern for the disposal or reuse of washwater than for consumer exposure
via food. The volatile DBPs represent the low-yield, final products
of chlorination reactions with multiple biomolecular precursors. The
initial, high-yield transformation products of such reactions may
represent a greater concern for consumer exposure because they remain
bound within the biopolymers in food and would be liberated during
digestion. Using protein-bound tyrosine as an example precursor, the
concentrations of the initial 3-chlorotyrosine and 3,5-dichlorotyrosine
transformation products from this one precursor in the leaf phase
were comparable to, and, in the case of some lettuces, exceeded, the
aggregate aqueous concentration of volatile DBPs formed from multiple
precursors. Chlorotyrosine formation increased when spinach was shredded
due to the greater accessibility of chlorine to proteins in the leaf
interiors. The cytotoxicity of chlorotyrosines to Chinese hamster
ovary cells was higher than any of the trihalomethanes regulated in
drinking water
Toxic Impact of Bromide and Iodide on Drinking Water Disinfected with Chlorine or Chloramines
Disinfectants inactivate
pathogens in source water; however, they
also react with organic matter and bromide/iodide to form disinfection
byproducts (DBPs). Although only a few DBP classes have been systematically
analyzed for toxicity, iodinated and brominated DBPs tend to be the
most toxic. The objectives of this research were (1) to determine
if monochloramine (NH<sub>2</sub>Cl) disinfection generated drinking
water with less toxicity than water disinfected with free chlorine
(HOCl) and (2) to determine the impact of added bromide and iodide
in conjunction with HOCl or NH<sub>2</sub>Cl disinfection on mammalian
cell cytotoxicity and genomic DNA damage induction. Water disinfected
with chlorine was less cytotoxic but more genotoxic than water disinfected
with chloramine. For both disinfectants, the addition of Br<sup>–</sup> and I<sup>–</sup> increased cytotoxicity and genotoxicity
with a greater response observed with NH<sub>2</sub>Cl disinfection.
Both cytotoxicity and genotoxicity were highly correlated with TOBr
and TOI. However, toxicity was weakly and inversely correlated with
TOCl. Thus, the forcing agents for cytotoxicity and genotoxicity were
the generation of brominated and iodinated DBPs rather than the formation
of chlorinated DBPs. Disinfection practices need careful consideration
especially when using source waters containing elevated bromide and
iodide
Development and Performance Characterization of a Polyamide Nanofiltration Membrane Modified with Covalently Bonded Aramide Dendrimers
A first generation of amine terminated
aramide dendrimers (G1-NH<sub>2</sub>) was covalently attached to
the polyamide (PA) active layer
of a commercially available nanofiltration (NF) membrane. Amide bonds
between G1-NH<sub>2</sub> and PA free carboxylic groups were formed
by activation of the carboxylic groups with 1-ethyl-3-(3-dimethylaminopropyl)
carbodiimide (EDC) or 2-chloro-1-methylpyridinium iodide (CMPI), followed
by aminolysis. Dendrimer attachment was assessed by indirectly measuring
the concentration of carboxylic groups and amine groups before and
after membrane modification with RBS using yttrium and tungstate ions
(Y<sup>3+</sup> and WO<sub>4</sub><sup>2‑</sup>) as ion probes. RBS
analyses showed a decrease in the concentration of carboxylic groups
and an increase in amine groups on the membrane active layer, consistent
with dendrimers attaching covalently to the active layer. Permeation
experiments with Rhodamine WT (R-WT) revealed that the water and solutes
permeability decreased after modification with dendrimer G1-NH<sub>2</sub>. Water permeability of G1-NH<sub>2</sub> modified membrane
decreased by 16–19% using EDC combined with sulfo-<i>N</i>-hydroxysuccinimide (s-NHS), and by 17–33% using CMPI. The
permeability of the electrolyte BaCl<sub>2</sub> decreased by 54%
after G1-NH<sub>2</sub> modification using EDC/s-NHS and only by 20%
using CMPI, the latter consistent with a weaker Donnan exclusion effect.
The permeability of the larger solute R-WT decreased by 82% in modified
G1-NH<sub>2</sub> membranes when using EDC/s-NHS, and 64% for cross-linking
reagent CMPI. Thus, the use of EDC/s-NHS was more favorable because
it resulted in higher gains in solute rejection with lower losses
in water permeability