Thesis (Ph. D.)--Princeton University, 1928.

Thesis (PH. D.)--Princeton University, 1928.

This study armed at the development of an adequate process for the odor control of a gas vented from a plant for treating olefin-resin manufacturing wastewater.The gas contains various aromatic and olefin compounds, such as toluene, £\-methyl styrene, vinyl toluene, styrene, naphthalene, dicyclopentadiene, and indene.Primary tests showed that these odorous compounds could not be effectively eliminated by a biotrickling filter packed with fern chips.Instead, these compounds can easily be removed or eliminated by using sodium hypochlorite as an oxidant and followed by sodium thiosulfate as a reductant for removing the residual chlorine odor. Results indicate that by scrubbing the gas with sodium hypochlorite solution with an effective residual chlorine of 40-60 mg/L, pH of 7.9-9.8, and oxidation-reduction potential (ORP) of 500-760 mV, concentration of volatile organic compounds (VOCs) in the test gas could be removed from 250 ppm (expressed as methane) to 23 ppm.Trace olefin and chlorine odors in the oxidized gas could further be removed by scrubbing it with an aqueous solution of 270 mg/L Na2S2O3.The overall VOC removal was around 92%.

Pharmaceutical compounds represent a rapidly emerging class of environmental contaminants. Such compounds were recently classified by the U.S. Geological Survey, including several antibiotics. An LC-MS/MS screening method for the top five antibiotics in drinking water was developed and validated using a Shimadzu LC-MS-IT-TOF. The separation was performed using a Waters Acquity UPLC BEH C18 column with a gradient elution. Sulfamethazine was exposed to conditions intended to mimic drinking water chlorination, and samples were collected and quenched with excess sodium sulfite. Kinetics of sulfamethazine degradation was followed as well as the formation of the major chlorinated byproduct (m/z 313). For the screening method, all five antibiotic peaks were baseline resolved within 5 minutes. Additionally, precision and accuracy of the screening method were less than 15%. Degradation of sulfamethazine upon exposure to drinking water chlorination occurred by first order kinetics with a half-life of 5.3 × 10(4) min (approximately 37 days) with measurements starting 5 minutes after chlorination. Likewise, the formation of the major chlorinated product occurred by first order kinetics with a rate constant of 2.0 × 10(-2). The proposed identification of the chlorinated product was 4-amino-(5-chloro-4,6-dimethyl-2-pyrimidinyl)-benzenesulfonamide (C12H13N4O2SCl) using MS (n) spectra and databases searches of SciFinder and ChemSpider.

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