PhD defense: Kiranmayi Mangalgiri
Location
The Commons : 329
Date & Time
April 25, 2017, 1:00 pm – 3:00 pm
Description
Kiranmayi Mangalgiri PhD Defense
Date: Tuesday, April 25th
Time: 1:00 pm
Location: Commons 329
Dissertation Title: Photolytic Fate of Antibiotics in UV-based Engineered and Natural Systems
Abstract:
Date: Tuesday, April 25th
Time: 1:00 pm
Location: Commons 329
Dissertation Title: Photolytic Fate of Antibiotics in UV-based Engineered and Natural Systems
Abstract:
Antibiotics
are used at high doses as feed additives in poultry operations.
However, most of the antibiotics ingested by poultry are excreted
unchanged. Since poultry litter is land applied as a fertilizer,
antibiotics are introduced into the environment. However, the photolytic
fate of antibiotics is not well characterized in agricultural systems.
This dissertation was designed to address two objectives: (i) to
characterize photodegradation of antibiotics in UV-based engineered
systems; and, (ii) to determine the photolytic fate of antibiotics in
agriculturally-relevant natural systems.
A
critical review on the detection, fate, and toxicity of organoarsenical
antibiotics, a relatively understudied group of feed additives in the
poultry industry, justified the need to conduct photodegradation studies
for this unique class of antibiotics. Irradiation experiments and
UV-H2O2 treatment at 253.7 nm for two organoarsenicals, roxarsone and
nitarsone, produced the pseudo-first-order fluence-based rate constants
in the range of 5.30-29.7×10-5 cm2 mJ-1, and second-order rate constants
for reaction with hydroxyl radicals as 3.40 (±0.45)×109 and
8.28(±0.49)×108 M-1 s-1 for roxarsone and nitarsone, respectively.
Bicarbonate and dissolved organic matter (DOM) from poultry litter
affected the transformation efficiency, and inorganic arsenic was
detected as a major byproduct.
The role of DOM
at elevated concentrations was evaluated for photolysis of four
representative antibiotics at 310 - 410 nm. The dominant mechanism for
ciprofloxacin degradation was direct photolysis; degradation of
roxarsone, chlortetracycline, and sulfamethoxazole was sensitized to
varying degrees as a function of DOM content and source due to
generation of reactive species. A parallel factor analysis of
fluorescence excitation emission matrices was used to describe the fate
of DOM in engineered and natural systems. Four components, microbial
humic-like, terrestrial humic-like, tyrosine-like, and tryptophan-like
fluorescence signatures were identified. In general, the tryptophan-like
component was more reactive than the humic-like components. The
tyrosine-like component was recalcitrant throughout all treatment
strategies. These components may be used to benchmark changes in
fluorescent DOM during treatment of agricultural waste.
This
dissertation reports critical knowledge on the complex photochemical
fate of antibiotics in agriculturally-impacted waters for UV-based
treatment processes, oxidation systems, and natural processes. The
information reported here will help address public health concerns over
the spread and development of antibiotic resistance.