Robert B. Young

Artificial Sweetener Sucralose in U.S. Drinking Water Systems

The artificial sweetener sucralose has recently been shown to be a widespread of contaminant of wastewater, surface water, and groundwater. In order to understand its occurrence in drinking water systems, water samples from 19 United States (U.S.) drinking water treatment plants (DWTPs) serving more than 28 million people were analyzed for sucralose using liquid chromatography tandem mass spectrometry (LC-MS/MS). Sucralose was found to be present in source water of 15 out of 19 DWTPs (47-2900 ng/L), finished water of 13 out of 17 DWTPs (49-2400 ng/L) and distribution system water of 8 out of the 12 DWTPs (48-2400 ng/L) tested. Sucralose was only found to be present in source waters with known wastewater influence and/or recreational usage, and displayed low removal (12% average) in the DWTPs where finished water was sampled. Further, in the subset of DWTPs with distribution system water sampled, the compound was found to persist regardless of the presence of residual chlorine or chloramines. In order to understand intra-DWTP consistency, sucralose was monitored at one drinking water treatment plant over an 11 month period from March 2010 through January 2011, and averaged 440 ng/L in the source water and 350 ng/L in the finished water. The results of this study confirm that sucralose will function well as an indicator compound for anthropogenic influence on source, finished drinking and distribution system (i.e., tap) water, as well as an indicator compound for the presence of other recalcitrant compounds in finished drinking water in the U.S.

Testosterone-mineralizing culture enriched from swine manure: characterization of degradation pathways and microbial community composition.

Environmental releases and fate of steroid sex hormones from livestock and wastewater treatment plants are of increasing regulatory concern. Despite the detection of these hormones in manures, biosolids, and the environment, little attention has been paid to characterization of fecal bacteria capable of hormone degradation. The enrichments of (swine) manure-borne bacteria capable of aerobic testosterone degradation were prepared and the testosterone mineralization pathway was elucidated. Six DNA sequences of bacteria from the Proteobacteria phylum distributed among the genera Acinetobacter, Brevundimonas, Comamonas, Sphingomonas, Stenotrophomonas, and Rhodobacter were identified in a testosterone-degrading enriched culture with testosterone as the sole carbon source. Three degradation products of testosterone were identified as androstenedione, androstadienedione, and dehydrotestosterone using commercially available reference standards, liquid chromatography-UV diode array detection, and liquid chromatography-time-of-flight mass spectrometry (LC-TOF/MS). Three additional degradation products of testosterone were tentatively identified as 9α-hydroxytestosterone, 9α-hydroxyandrostadienedione or 3-hydroxy-9,10-secoandrosta-1,3,5(10)-triene-9,17-dione, and 9α-hydroxydehydrotestosterone or 9α-hydroxyandrostenedione using LC-TOF/MS. When (14)C-testosterone was introduced to the enriched culture, 49-68% of the added (14)C-testosterone was mineralized to (14)CO(2) within 8 days of incubation. The mineralization of (14)C-testosterone followed pseudo-first-order reaction kinetics in the enriched culture with half-lives (t(1/2)) of 10-143 h. This work suggests that Proteobacteria play an important environmental role in degradation of steroid sex hormones and that androgens have the potential to be mineralized during aerobic manure treatment or after land application to agricultural fields by manure-borne bacteria.

Direct photodegradation of androstenedione and testosterone in natural sunlight: inhibition by dissolved organic matter and reduction of endocrine disrupting potential.

In surface waters, two of the most commonly observed androgenic steroid hormones are androstenedione (AD) and testosterone (T). This study compares the photodegradation of dilute (<10 μg L(-1)) aqueous solutions of AD and T in natural sunlight, and evaluates the endocrine-disrupting potential of the resulting solutions. This study also examines the effect of dissolved organic matter (DOM) on AD photodegradation. During spring and summer at Henderson, NV, USA (latitude 36.04°N), AD and T underwent direct photodegradation, with half-lives ranging from 3.7 to 10.8 h. In three model DOM solutions, ADs half-life increased by 11% to 35%. Using screening factors to eliminate DOMs inner filter effect, quantum yield calculations suggested that light screening was primarily responsible for ADs increased half-life, and that physical quenching further inhibited ADs photodegradation in two out of three DOM solutions. In vitro androgenic activity of the AD and T solutions decreased approximately as fast as AD and T were removed, suggesting that solar photodegradation reduces the risk of endocrine disruption in surface waters impacted by AD or T, subject to continuing inputs. Reduced in vitro androgenic activity appears to be related to steroid ring cleavage and the formation of highly oxidized photoproducts.

Two New Methods of Synthesis for the Perbromate Ion: Chemistry and Determination by LC-MS/MS

Historically, the synthesis of perbromate ion through conventional oxidation routes has proven elusive. Herein, we report perbromate ion formation through the reaction of hypobromite and bromate ions in an alkaline sodium hypobromite solution. Formation was established via LC-MS/MS analysis of the bromate and perbromate ions in the reaction solutions over a 13-day period. Furthermore, it was discovered that the perbromate ion was also formed as a result of the electrospray ionization process. Selective reduction of the bromate ion prior to analysis was used to confirm the two formation pathways.