Models for Design of Upflow Anaerobic Filters Separated in Two and Three Phases

AbstractThis research presents two hybrid models based on the Streter-Phelps equation associated with nonstationary conditions dS/dt≠0 and advective dS/dZ≠0, statistically adjusted and applicable for the design of anaerobic upflow filters separated in two and three phases, operated on a laboratory s...

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Veröffentlicht in:Journal of environmental engineering (New York, N.Y.) N.Y.), 2020-03, Vol.146 (3)
Hauptverfasser: Maldonado Maldonado, Julio Isaac, Márquez Romance, Adriana Mercedes, Guevara Pérez, Edilberto, José Rey Lago, Demetrio, Pérez Pacheco, Sergio Alejandro
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container_issue 3
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container_title Journal of environmental engineering (New York, N.Y.)
container_volume 146
creator Maldonado Maldonado, Julio Isaac
Márquez Romance, Adriana Mercedes
Guevara Pérez, Edilberto
José Rey Lago, Demetrio
Pérez Pacheco, Sergio Alejandro
description AbstractThis research presents two hybrid models based on the Streter-Phelps equation associated with nonstationary conditions dS/dt≠0 and advective dS/dZ≠0, statistically adjusted and applicable for the design of anaerobic upflow filters separated in two and three phases, operated on a laboratory scale using landfill leachate as substrate under a 33 experimental factorial design. The factors included (1) volumetric organic load (VOL)=2.25, 3.45, and 4.64  kg CODm−3day−1 [chemical oxygen demand (COD)]; (2) temperature (T)=20°C, 27°C, and 34°C; and (3) height ratios (D1 = height phase 1, D2 = height phase 2, and D3 = height phase); DI-FAFS (Spanish acronym that means Upflow Anaerobic Filter separated in Two Phases):  D1/D2=20%/80%, 50%/50%, and 80%/20%, and TRI-FAFS (upflow anaerobic filter separated in three phases): D1/D2/D3=4%/16%/80%, 10%/10%/80%, and 16%/4%/80%. Operating conditions included (1) hydraulic retention time (HRT) between 16 and 18 h; (2) flow rates of 3.5–4.0  mL min−1; (3) surface hydraulic load of 1.82  m3  m−2 day−1; and (4) filter total depth of 1.2 m, filled with plastic material with a specific surface area of 476.35  m2m−3. Fifty-four tests were performed, obtaining efficiency between 27% and 73% in the DI-FAFS and between 84% and 94% in the TRI-FAFS (Spanish acronym that means Upflow Anaerobic Filter separated in Three Phases). Maximum efficiencies were achieved with D1/D2 ratios 20%/80% and D1/D2/D3=10%/10%/80%, respectively, with temperatures ≥27°C and VOL≥3.45  kgCODm−3day−1.
doi_str_mv 10.1061/(ASCE)EE.1943-7870.0001577
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The factors included (1) volumetric organic load (VOL)=2.25, 3.45, and 4.64  kg CODm−3day−1 [chemical oxygen demand (COD)]; (2) temperature (T)=20°C, 27°C, and 34°C; and (3) height ratios (D1 = height phase 1, D2 = height phase 2, and D3 = height phase); DI-FAFS (Spanish acronym that means Upflow Anaerobic Filter separated in Two Phases):  D1/D2=20%/80%, 50%/50%, and 80%/20%, and TRI-FAFS (upflow anaerobic filter separated in three phases): D1/D2/D3=4%/16%/80%, 10%/10%/80%, and 16%/4%/80%. Operating conditions included (1) hydraulic retention time (HRT) between 16 and 18 h; (2) flow rates of 3.5–4.0  mL min−1; (3) surface hydraulic load of 1.82  m3  m−2 day−1; and (4) filter total depth of 1.2 m, filled with plastic material with a specific surface area of 476.35  m2m−3. Fifty-four tests were performed, obtaining efficiency between 27% and 73% in the DI-FAFS and between 84% and 94% in the TRI-FAFS (Spanish acronym that means Upflow Anaerobic Filter separated in Three Phases). 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The factors included (1) volumetric organic load (VOL)=2.25, 3.45, and 4.64  kg CODm−3day−1 [chemical oxygen demand (COD)]; (2) temperature (T)=20°C, 27°C, and 34°C; and (3) height ratios (D1 = height phase 1, D2 = height phase 2, and D3 = height phase); DI-FAFS (Spanish acronym that means Upflow Anaerobic Filter separated in Two Phases):  D1/D2=20%/80%, 50%/50%, and 80%/20%, and TRI-FAFS (upflow anaerobic filter separated in three phases): D1/D2/D3=4%/16%/80%, 10%/10%/80%, and 16%/4%/80%. Operating conditions included (1) hydraulic retention time (HRT) between 16 and 18 h; (2) flow rates of 3.5–4.0  mL min−1; (3) surface hydraulic load of 1.82  m3  m−2 day−1; and (4) filter total depth of 1.2 m, filled with plastic material with a specific surface area of 476.35  m2m−3. Fifty-four tests were performed, obtaining efficiency between 27% and 73% in the DI-FAFS and between 84% and 94% in the TRI-FAFS (Spanish acronym that means Upflow Anaerobic Filter separated in Three Phases). Maximum efficiencies were achieved with D1/D2 ratios 20%/80% and D1/D2/D3=10%/10%/80%, respectively, with temperatures ≥27°C and VOL≥3.45  kgCODm−3day−1.</abstract><cop>New York</cop><pub>American Society of Civil Engineers</pub><doi>10.1061/(ASCE)EE.1943-7870.0001577</doi><orcidid>https://orcid.org/0000-0002-5956-5917</orcidid></addata></record>
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source American Society of Civil Engineers:NESLI2:Journals:2014
subjects Chemical oxygen demand
Design
Design factors
Factorial design
Filters
Flow rates
Flow velocity
Fluid filters
Hydraulic loading
Hydraulic retention time
Landfills
Leachates
Organic chemistry
Organic loading
Phases
Retention time
Substrates
Technical Papers
Waste disposal sites
title Models for Design of Upflow Anaerobic Filters Separated in Two and Three Phases
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