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Contaminant Transport and Filtration Issues with DOAS. ASHRAE Louisville Meeting June 23, 2009. Stanley A. Mumma, Ph.D., P.E. Prof. Emeritus, Architectural Engineering Penn State University, Univ. Park, PA sam11@psu.edu. Web: http://doas-radiant.psu.edu. Objective.
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Contaminant Transportand Filtration Issueswith DOAS ASHRAE Louisville MeetingJune 23, 2009 Stanley A. Mumma, Ph.D., P.E. Prof. Emeritus, Architectural Engineering Penn State University, Univ. Park, PA sam11@psu.edu Web: http://doas-radiant.psu.edu
Objective • Dispel the common perception that DOAS is inferior to all air system when contaminant flushing rates from occupied spaces are considered. • Shift the DOAS filter selection paradigm.
DOAS Defined High Induction Diffuser Cool/Dry Supply OA DOAS Unit w/ TER, CC, & Filtration RA Building with Sensible and Latent Cooling Decoupled Parallel Sensible Cooling System
Facility floor area and zoning for case study 1,000 ft2 Exterior Zone 1 9,000 ft2 Exterior Zone 2 10,000 ft2 Interior Zone 3 10 ft high ceilings--all zones
Case Study Conditions • VAV system: • Supply air (SA) flow rate, 16,000 cfm, of which 4,000 cfm is OA. • Perimeter zones 1 and 2, each receives 1 cfm/ft2 of supply air via a shut off box VAV system. Since the SA is 25% OA, then each perimeter zone is receiving 0.25 cfm/ft2. • Interior zone 3 receives 0.6 cfm/ft2 of supply air via a VAV system, i.e. 0.15 cfm/ft2 OA • DOAS: • OA flow for the facility, 4,000 cfm uniformly distributed in each zone, or 0.20 cfm/ft2.
Transient analysis is based upon the following simplifying assumptions: • Well mixed zones. • No interzonal transfer. • Contaminants stay suspended. • VAV system is analyzed while operating in the minimum OA mode (4,000 cfm OA), and a supply airflow rate of 16,000 cfm. Releases during full economizer mode (resulting in very high peak space concentrations when releases occur near the OA inlet) will not be presented. • The capacitance of the duct system, and its associated influence on the transient response, is neglected.
VAV System Schematic Filter, hf 3 2 1
DOAS Schematic Filter, hf 3 2 1
Transient dimensionless concent’n from release near OA inlet w/ hf = 0% VAV Zone 1 & 2 DOAS VAV Zone 3
Transient concent’n from release near OA inlet w/ VAV hf = 80% & DOAS hf = 98% NOTE: Exposurew/ DOAS is 1/425that of VAV. VAV Zone 1 & 2 VAV Zone 3 DOAS
DOAS filter h necessary to match the space concent’n/exposure after 60 min. for a given VAV filter h. Ref: OA intake occurances. = conc. Paradigm shift!! = h = exp
Filter Optimization Assumptions • Same SA flows as in transient analysis: VAV 16,000 cfm; and DOAS 4,000 cfm. • Assume that the filter loading profile is exponential, causing the average pressure drop over the life of the filter to be:[(Dploaded opt - Dpclean opt)/2]*Fill-ratio. 0.87 Fill-ratio used. • Reference replacement frequency is 3 months for VAV and 6 months for DOAS • fan/motor combined efficiency, 60%. • Electrical cost, $0.10/kWh. • Term of analysis, 5 years. • Fan operating hours per year, 4160 hours. • Neglect the time value of money and inflation.
Filters used in the Optimization Merv 13& 14 Filter94 & 98% h Merv 11 Filter75% h Merv 16 Filter99.7% h
Conclusions • A common attitude that contaminant flushing is a problem with DOASs is not warranted when the proper DOAS filter is selected, i.e. one better than the filter used in a comparably performing VAV system. • The old “equivalence” paradigm needs to change. • Guidance is offered, at least for one set of conditions, on DOAS filter efficiencies. And a method is provided for use on other sets of conditions. • Finally, contrary to conventional wisdom, the selection of better and more expensive DOAS filters resulted in optimized performance costing less— far less —than VAV systems.