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Nonylphenol Degradation During Wastewater Treatment - Importance of Nitrifying Bacteria. Presented By: Natasha Sinha. Comparison of 4 Compounds: Compound (Use and Effect) C MAX (µg/L) Days to Med Dose Caffeine (stimulant) 5.7 5.7 x 10 3 (Excedrin Migraine)
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Nonylphenol Degradation During Wastewater Treatment - Importance of Nitrifying Bacteria Presented By: Natasha Sinha
Comparison of 4 Compounds: • Compound (Use and Effect)CMAX (µg/L)Days to Med Dose • Caffeine (stimulant) 5.7 5.7 x 103 (Excedrin Migraine) • Ibuprofen (anti-inflammatory) 1.0 105 (Motrin) • 17α-ethinyl estradiol (oral contraceptive) 0.27 37 (Alesse-21) • 17β-estradiol (vertebrate hormone) 0.093 (Phoenix) 5.3 x 103 (Activella) • 4-nonylphenol (surfactant metabolite) 40 (Tucson) 4.6 x 10-4 as estrogenic E2, EE2 Motivation: USGS Surface Water Reconnaissance(Kolpin et al., 2002) Sampling regions for the USGS Reconnaissance of US surface water
Further Motivation:Intersex Characteristics in Fish Populations These data represent the frequency of intersex characteristics of fish taken above and below wastewater treatment discharges
Background on Ammonia Oxidizing Bacteria • NH4+ NH2OH NO2 O2 AMO (ammonia monoxygenase) AMO is a non-selective monoxygenase • Central Hypothesis: Estrogen removal is due to AMO activity in culture.
Lab Setup Synthetic Wastewater Control Unit Clarified Effluent Reactor Variable: Sludge Age
Experimental Procedure Part 1 • Step 1: Look for NH4+ stimulation of O2 use • Determine whether ammonia oxidizing bacteria are present.
Result (1) OUR: 0.00054 OUR:0.00059 OUR: 0.00025 OUR: Oxygen Utilization Rate
Was Nonylphenol Degraded? Measurements of nonylphenol degradation were taken after 24 hours and 48 hours using a C-18 procedure and Gas Chromatography
To Come • Repeat with longer sludge retention time • Compare to previous results • Supplement with effluent NH4+ data
Acknowledgements Dr. Robert Arnold Dave Newman Bingfeng Dong Dustin Brown & Arthur Ho