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Presented By: Natasha Sinha
Nonylphenol Degradation During Wastewater Treatment - Importance of Nitrifying Bacteria Presented By: Natasha Sinha
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Motivation: USGS Surface Water Reconnaissance (Kolpin et al., 2002)
Comparison of 4 Compounds: Compound (Use and Effect) CMAX (µg/L) Days to Med Dose Caffeine (stimulant) x 103 (Excedrin Migraine) Ibuprofen (anti-inflammatory) (Motrin) 17α-ethinyl estradiol (oral contraceptive) (Alesse-21) 17β-estradiol (vertebrate hormone) (Phoenix) 5.3 x 103 (Activella) 4-nonylphenol (surfactant metabolite) (Tucson) 4.6 x 10-4 as estrogenic E2, EE2 Sampling regions for the USGS Reconnaissance of US surface water
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Secondary Effluent Chromotograph
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Further Motivation: Intersex Characteristics in Fish Populations
These data represent the frequency of intersex characteristics of fish taken above and below wastewater treatment discharges
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Relative Estrogenic Activity
Known Estrogenic Compounds in Wastewater Chemical Structure Molecular Weight Log Kow Relative Estrogenic Activity (YES bioassay) 17-estradiol (E2) 272.39 3.94(9) 1.0 17-ethinyl estradiol (EE2) 296.40 4.15(9) 1.32 Estrone (E1) 270.37 3.43(9) 0.20 Estriol (E3) 288.39 2.81(9) 0.01 Nonylphenol (NP) 220.35 4.48(10) 2×10-4 Octylphenol (OP) 206.33 4.12(10) 3×10-4 Bisphenol A (BPA) 228.29 3.40(11) 8 x 10-5
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Conventional Wastewater Treatment Processes
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Removal of Estrogens in Arizona Plants
Total Estrogenic Activity (M as EE2) Facility Influent Effluent Fraction Removal Avra Valley 1 x 10-9 2 x 10-12 0.998 Roger Road 3 x 10-10 2 x 10-10 0.33 Ina Road 4 x 10-11 5 x 10-12 0.88 Randolph Park < 2 x 10-12 > 0.99 Wildcat 1 x 10-10 4 x 10-12 0.96 Rio de Flag 1.5 x 10-10 < 6 x 10-13 > 0.996
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Background on Ammonia Oxidizing Bacteria
NH NH2OH NO2 O AMO (ammonia monoxygenase) AMO is a non-selective monoxygenase Central Hypothesis: Estrogen removal is due to AMO activity in culture.
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Lab Setup Synthetic Wastewater Control Unit Clarified Effluent Reactor
Variable: Sludge Age
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Experimental Procedure Part 1
Step 1: Look for NH4+ stimulation of O2 use Determine whether ammonia oxidizing bacteria are present.
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Result (1) OUR: Oxygen Utilization Rate OUR: 0.00054 OUR: 0.00059
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Was Nonylphenol Degraded?
Measurements of nonylphenol degradation were taken after 24 hours and 48 hours using a C-18 procedure and Gas Chromatography No NP + NP No ATU + ATU
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Removal of Nonylphenol + Data
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To Come Repeat with longer sludge retention time
Compare to previous results Supplement with effluent NH4+ data
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Dustin Brown & Arthur Ho
Acknowledgements Dr. Robert Arnold Dave Newman Bingfeng Dong Dustin Brown & Arthur Ho
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