9 research outputs found
Degradation of Antibiotic Activity during UV/H<sub>2</sub>O<sub>2</sub> Advanced Oxidation and Photolysis in Wastewater Effluent
Trace
levels of antibiotics in treated wastewater effluents may
present a human health risk due to the rise of antibacterial activity
in the downstream environments. Advanced oxidation has a potential
to become an effective treatment technology for transforming trace
antibiotics in wastewater effluents, but residual or newly generated
antibacterial properties of transformation products are a concern.
This study demonstrates the effect of UV photolysis and UV/H<sub>2</sub>O<sub>2</sub> advanced oxidation on transformation of 6 antibiotics,
each a representative of a different structural class, in pure water
and in two different effluents and reports new or confirmatory photolysis
quantum yields and hydroxyl radical rate constants. The decay of the
parent compound was monitored with HPLC/ITMS, and the corresponding
changes in antibacterial activity were measured using bacterial inhibition
assays. No antibacterially active products were observed following
treatment for four of the six antibiotics (clindamycin, ciprofloxacin,
penicillin-G, and trimethoprim). The remaining two antibiotics (erythromycin
and doxycycline) showed some intermediates with antibacterial activity
at low treatment doses. The antibacterially active products lost activity
as the UV dose increased past 500 mJ/cm<sup>2</sup>. Active products
were observed only in wastewater effluents and not in pure water,
suggesting that complex secondary reactions controlled by the composition
of the matrix were responsible for their formation. This outcome emphasizes
the importance of bench-scale experiments in realistic water matrices.
Most importantly, the results indicate that photosensitized processes
during high dose wastewater disinfection may be creating antibacterially
active transformation products from some common antibiotics
Life Cycle Environmental Impacts of Disinfection Technologies Used in Small Drinking Water Systems
Small drinking water systems serve
a fifth of the U.S. population
and rely heavily on disinfection. While chlorine disinfection is common,
there is interest in minimizing chemical addition, especially due
to carcinogenic disinfection byproducts and chlorine-resistant pathogens,
by using ultraviolet technologies; however, the relative, broader
environmental impacts of these technologies are not well established,
especially in the context of small (<10 000 people) water
systems. The objective of this study was to identify environmental
trade-offs between chlorine and ultraviolet disinfection via comparative
life cycle assessment. The functional unit was the production of 1
m<sup>3</sup> of drinking water to U.S. standards. Treatment included
cartridge filtration followed by either chlorine disinfection or ultraviolet
disinfection with chlorine residual addition. Environmental performance
was evaluated for various chlorine contact zone materials (plastic,
concrete, steel), ultraviolet validation factors (1.2 to 4.4), and
electricity sources (renewable; U.S. average, high, and low impact
grids). Performance was also evaluated when filtration and chlorine
residual were not required. From a life cycle assessment perspective,
replacing chlorine with UV was preferred only in a limited number
of cases (i.e., high pumping pressure but filtration is not required).
In all others, chlorine was environmentally preferred, although some
contact zone materials and energy sources had an impact on the comparison.
Utilities can use these data to inform their disinfection technology
selection and operation to minimize environmental and human health
impacts
Wavelength-Dependent Damage to Adenoviral Proteins Across the Germicidal UV Spectrum
Adenovirus,
a waterborne pathogen responsible for causing bronchitis,
pneumonia, and gastrointestinal infections, is highly resistant to
UV disinfection and therefore drives the virus disinfection regulations
set by the U.S. Environmental Protection Agency. Polychromatic UV
irradiation has been shown to be more effective at inactivating adenovirus
and other viruses than traditional monochromatic irradiation emitted
at 254 nm; the enhanced efficacy has been attributed to UV-induced
damage to viral proteins. This research shows UV-induced damage to
adenoviral proteins across the germicidal UV spectrum at wavelength
intervals between 200 and 300 nm. A deuterium lamp with bandpass filters
and UV light-emitting diodes (UV LEDs) isolated wavelengths in approximate
10 nm intervals. Sodium dodecyl sulfate polyacrylamide gel electrophoresis
and image densitometry were used to detect signatures for the hexon,
penton, fiber, minor capsid, and core proteins. The greatest loss
of protein signature, indicating damage to viral proteins, occurred
below 240 nm. Hexon and penton proteins exposed to a dose of 28 mJ/cm<sup>2</sup> emitted at 214 nm were approximately 4 times as sensitive
and fiber proteins approximately 3 times as sensitive as those exposed
to a dose of 50 mJ/cm<sup>2</sup> emitted at 254 nm. At 220 nm, a
dose of 38 mJ/cm<sup>2</sup> reduced the hexon and penton protein
quantities to approximately 33% and 31% of the original amounts, respectively.
In contrast, a much higher dose of 400 mJ/cm<sup>2</sup> emitted at
261 and 278 nm reduced the original protein quantity to between 66–89%
and 80–93%, respectively. No significant damage was seen with
a dose of 400 mJ/cm<sup>2</sup> at 254 nm. This research directly
correlates enhanced inactivation at low wavelengths with adenoviral
protein damage at those wavelengths, adding fundamental insight into
the mechanisms of inactivation of polychromatic germicidal UV irradiation
for improving UV water disinfection
A Pilot Household Greywater Treatment and Reuse System Produces High-Quality Water under Simulated Household Illness Test Conditions
As
water scarcity and plumbing challenges continue to affect small
and rural communities, direct potable reuse has the potential to improve
household access to clean, potable water. A pilot household greywater
reuse system was built and operated daily for nine months to determine
whether high-quality water that was safe for human contact could be
produced consistently on site. Sixty gallons of water were produced
per day under normal and stress conditions, including a simulated
whole household illness when viruses were spiked into the system to
attempt to overwhelm the effectiveness of the treatment. The system
produced high-quality potable water for more than 2 weeks, requiring
the addition and removal of only 30 gal of outside water weekly for the household to have 420
gal of treated water available each week and meeting recommended virus
reduction standards for small and household-level direct potable reuse
systems. Wash water had a low level of total organic carbon, low turbidity,
and low conductivity, normal pH, and high ultraviolet transmittance.
The treatment process train provided >18 log10 reduction
of viruses and >8 log10 reduction of bacteria. While
the
system produced sufficient wash water to protect health, the concentrated
wastes produced could pose a threat to the household if proper waste
disposal methods are not facilitated
Production of Photo-oxidants by Dissolved Organic Matter During UV Water Treatment
Dissolved organic matter (DOM) irradiated
by sunlight generates
photo-oxidants that can accelerate organic contaminant degradation
in surface waters. However, the significance of this process to contaminant
removal during engineered UV water treatment has not been demonstrated,
partly due to a lack of suitable methods in the deep UV range. This
work expands methods previously established to detect <sup>1</sup>O<sub>2</sub>, HO•, H<sub>2</sub>O<sub>2</sub>, and DOM triplet
states (<sup>3</sup>DOM*) at solar wavelengths to irradiation at 254
nm, typical of UV water treatment. For transient intermediates, the
methods include a photostable probe combined with selective scavengers.
Quantum yields for <sup>1</sup>O<sub>2</sub>, <sup>3</sup>DOM* and
H<sub>2</sub>O<sub>2</sub> were in the same range as for solar-driven
reactions but were an order of magnitude higher for HO•, which
other experiments indicate is due to H<sub>2</sub>O<sub>2</sub> reduction.
With the quantum yields, the degradation of metoxuron was successfully
predicted in a DOM solution irradiated at 254 nm. Further modeling
showed that the contribution of DOM sensitization to organic contaminant
removal during UV treatment should be significant only at high UV
fluence, characteristic of advanced oxidation processes. Of the reactive
species studied, <sup>3</sup>DOM* is predicted to have the greatest
general influence on UV degradation of contaminants
Organic Chemical Characterization and Mass Balance of a Hydraulically Fractured Well: From Fracturing Fluid to Produced Water over 405 Days
A long-term
field study (405 days) of a hydraulically fractured
well from the Niobrara Formation in the Denver-Julesburg Basin was
completed. Characterization of organic chemicals used in hydraulic
fracturing and their changes through time, from the preinjected fracturing
fluid to the produced water, was conducted. The characterization consisted
of a mass balance by dissolved organic carbon (DOC), volatile organic
analysis by gas chromatography/mass spectrometry, and nonvolatile
organic analysis by liquid chromatography/mass spectrometry. DOC decreased
from 1500 mg/L in initial flowback to 200 mg/L in the final produced
water. Only ∼11% of the injected DOC returned by the end of
the study, with this 11% representing a maximum fraction returned
since the formation itself contributes DOC. Furthermore, the majority
of returning DOC was of the hydrophilic fraction (60–85%).
Volatile organic compound analysis revealed substantial concentrations
of individual BTEX compounds (0.1–11 mg/L) over the 405-day
study. Nonvolatile organic compounds identified were polyethylene
glycols (PEGs), polypropylene glycols (PPG), linear alkyl-ethoxylates,
and triisopropanolamine (TIPA). The distribution of PEGs, PPGs, and
TIPA and their ubiquitous presence in our samples and the literature
illustrate their potential as organic tracers for treatment operations
or in the event of an environmental spill
Enhanced Biodegradation of Carbamazepine after UV/H<sub>2</sub>O<sub>2</sub> Advanced Oxidation
Carbamazepine is one of the most persistent pharmaceutical
compounds
in wastewater effluents due to its resistance to biodegradation-based
conventional treatment. Advanced oxidation can efficiently degrade
carbamazepine, but the toxicity and persistence of the oxidation products
may be more relevant than the parent. This study sets out to determine
whether the products of advanced oxidation of carbamazepine can be
biotransformed and ultimately mineralized by developing a novel methodology
to assess these sequential treatment processes. The methodology traces
the transformation products of the <sup>14</sup>C-labeled carbamazepine
during UV/hydrogen peroxide advanced oxidation and subsequent biotransformation
by mixed, undefined cultures using liquid scintillation counting and
liquid chromatography with radioactivity, mass spectrometry, and UV
detectors. The results show that the oxidation byproducts of carbamazepine
containing a hydroxyl or carbonyl group can be fully mineralized by
a mixed bacterial inoculum. A tertiary treatment approach that includes
oxidation and biotransformation has the potential to synergistically
mineralize persistent pharmaceutical compounds in wastewater treatment
plant effluents. The methodology developed for this study can be applied
to assess the mineralization potential of other persistent organic
contaminants
Application of Metabolite Profiling Tools and Time-of-Flight Mass Spectrometry in the Identification of Transformation Products of Iopromide and Iopamidol during Advanced Oxidation
The efficiency of wastewater treatment
systems in removing pharmaceuticals
is often assessed on the basis of the decrease in the concentration
of the parent compound. However, what is perceived as “removal”
during treatment may not necessarily mean mineralization of the pharmaceutical
compound but simply conversion into different transformation products
(TPs). Using liquid chromatography coupled to a quadrupole time-of-flight
mass spectrometer (LC-QToF-MS), we demonstrated conversion of iopromide
in wastewater to at least 14 TPs after an advanced oxidation process
(AOP) using UV (fluence = 1500 mJ/cm<sup>2</sup>) and H<sub>2</sub>O<sub>2</sub> (10 mg/L). Due to the complexity of the wastewater
matrix, the initial experiments were performed using a high concentration
(10 mg/L) of iopromide in order to facilitate the identification of
TPs. Despite the high concentration of iopromide used, cursory inspection
of UV and mass spectra only revealed four TPs in the chromatograms
of the post-AOP samples. However, the use of METLIN database and statistics-based
profiling tools commonly used in metabolomics proved effective in
discriminating between background signals and TPs derived from iopromide.
High-resolution mass data allowed one to predict molecular formulas
of putative TPs with errors below 5 ppm relative to the observed <i>m</i>/<i>z</i>. Tandem mass spectrometry (MS/MS) data
and isotope pattern comparisons provided necessary information that
allowed one to elucidate the structure of iopromide TPs. The presence
of the proposed iopromide TPs was determined in unspiked wastewater
from a municipal wastewater treatment plant, but no iopromide and
TPs were detected. Using analogous structural modifications and oxidation
that results from the AOP treatment of iopromide, the potential TPs
of iopamidol (a structurally similar compound to iopromide) were predicted.
The same mass fragmentation pattern observed in iopromide TPs was
applied to the predicted iopamidol TPs. LC-QToF-MS revealed the presence
of two iopamidol TPs in unspiked AOP-treated wastewater
Wavelength Dependent UV Inactivation and DNA Damage of Adenovirus as Measured by Cell Culture Infectivity and Long Range Quantitative PCR
Adenovirus is regarded as the most
resistant pathogen to ultraviolet
(UV) disinfection due to its demonstrated resistance to monochromatic,
low-pressure (LP) UV irradiation at 254 nm. This resistance has resulted
in high UV dose requirements for all viruses in regulations set by
the United States Environmental Protection Agency. Polychromatic,
medium-pressure (MP) UV irradiation has been shown to be much more
effective than 254 nm, although the mechanisms of polychromatic UV
inactivation are not completely understood. This research analyzes
the wavelength-specific effects of UV light on adenovirus type 2 by
analyzing in parallel the reduction in viral infectivity and damage
to the viral genome. A tunable laser from the National Institute of
Standards and Technology was used to isolate single UV wavelengths.
Cell culture infectivity and PCR were employed to quantify the adenoviral
inactivation rates using narrow bands of irradiation (<1 nm) at
10 nm intervals between 210 and 290 nm. The inactivation rate corresponding
to adenoviral genome damage matched the inactivation rate of adenovirus
infectivity at 253.7 nm, 270 nm, 280 nm, and 290 nm, suggesting that
damage to the viral DNA was primarily responsible for loss of infectivity
at those wavelengths. At 260 nm, more damage to the nucleic acid was
observed than reduction in viral infectivity. At 240 nm and below,
the reduction of viral infectivity was significantly greater than
the reduction of DNA amplification, suggesting that UV damage to a
viral component other than DNA contributed to the loss of infectivity
at those wavelengths. Inactivation rates were used to develop a detailed
spectral sensitivity or action spectrum of adenovirus 2. This research
has significant implications for the water treatment industry with
regard to polychromatic inactivation of viruses and the development
of novel wavelength-specific UV disinfection technologies