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RECORD NUMBER: 6 OF 20

Main Title Destruction of Spores on Building Decontamination Residue in a Commercial Autoclave.
Author Sieber, R. ; Osborne, A. ; Lemieux, P. ;
CORP Author Eastern Research Group, Inc., Chantilly, MA. ;Environmental Protection Agency, Research Triangle Park, NC. National Homeland Security Research Center.
Publisher Apr 2005
Year Published 2005
Report Number EPA/600/R-05/081;
Stock Number PB2006-106777
Additional Subjects Buildings ; Decontamination ; Autoclaves ; Spores ; Biological weapons ; Contamination ; Residues ; Sterilization ; Wallboard ; Carpet ; Building decontamination residue ; Ceiling tiles ; Upholstered furniture
Internet Access
Description Access URL
https://nepis.epa.gov/Exe/ZyPDF.cgi?Dockey=90150O00.PDF
Holdings
Library Call Number Additional Info Location Last
Modified
Checkout
Status
NTIS  PB2006-106777 Some EPA libraries have a fiche copy filed under the call number shown. 07/26/2022
Collation 86p
Abstract
In the event of a terrorist attack on a building where biological weapons such as anthrax might be used, much of the porous material in the building will be shipped for disposal after decontamination activities. This material is collectively termed 'building decontamination residue' (BDR). Although the BDR will have been disinfected or decontaminated, it is possible that residual biological agent will remain in the material. Autoclaves are commonly used to sterilize regulated medical waste by exposing the waste to elevated pressures and temperatures for extended periods of time (e.g., 31.5 psig, 275 deg F, and 40 minutes). However, some types of BDR may be densely packed or have low thermal conductivity and may require longer periods of time to reach the operating temperature of an autoclave. This report addresses whether the standard operating procedure in a commercial autoclave will provide sufficient time/temperature/pressure to adequately destroy bacteria spores bound on BDR. This study investigated the effect of several variables related to autoclaving BDR, including time, temperature, pressure, item type, moisture content, packing density, packing orientation, autoclave bag integrity, and autoclave process sequence. The test team created simulated BDR from wallboard, ceiling tiles, carpet, and upholstered furniture, embedded with 10(sup 6) population Geobacillus stearothermophilus biological indicator (BI) strips and thermocouples to obtain time/temperature profile data associated with each BI strip. Study results indicate that bags of BDR should be placed in an autoclave so that all sides of individual bags are exposed to autoclave conditions, and not nested or stacked in a manner that precludes full exposure. All materials tested were effectively sterilized when dry. Increasing moisture content made autoclaving more difficult, but wet wallboard and ceiling tiles were also effectively sterilized. Autoclave cycles of 120 minutes at 31.5 psig/ 275 deg F and 75 minutes at 45 psig/ 292 deg F effectively sterilized the BDR material. Two standard autoclave cycles of 40 minutes and 31.5 psig/ 275 deg F run in sequence proved to be particularly effective, probably because the second cycle's evacuation step pulled the condensed water out of the pores of the materials, allowing effective steam penetration.