Seven species of bacterial biothreat agents were tested for susceptibility to UV light (254 nm). All gramnegative organisms tested required <12 mJ/cm 2 for a 4-log 10 reduction in viability (inactivation). Tailing off of the B. anthracis spore inactivation curves began close to the 2-log 10 inactivation point, with a fluence of approximately 40 mJ/cm 2 , and 3-log 10 inactivation still was not achieved with a fluence of 120 mJ/cm 2 .The security of our nation's water supply is a concern for water providers and public health officials. Questions have been asked regarding the possibility of our drinking water becoming contaminated with biothreat agents and the efficacy of current disinfection practices for the reduction in viability (inactivation) of biothreat agents (5,8,14). The use of UV irradiation as a supplemental water disinfection practice is increasing for several reasons, among them improving control of protozoa, such as Cryptosporidium spp., and decreasing disinfection by-products created by chemical disinfectants (21 anthracis was grown on soil extract-peptone-beef extract agar (SEA) (1) or in Schaeffer's sporulation medium (SSM) (10) for 7 days, resulting in Ͼ99% spores as determined by phase-contrast microscopy. The cells and spores were then washed by centrifugation (8,000 ϫ g), resuspended in ultrapure water, transferred to centrifuge tubes, treated with 50% ethanol for 1 h at room temperature, and washed five times with sterile ultrapure water before being stored in reverse-osmosis water at Ϫ70°C. F. tularensis isolates were grown on cysteine heart agar (1) and all other isolates on Trypticase soy agar with 5% sheep blood (TSA II; Becton Dickinson Microbiology Systems, Sparks, MD) for 24 h before testing. B. anthracis spores were adjusted to 10 7 CFU/ml and other bacterial suspensions to 10 8 CFU/ml in Butterfield buffer (3 mM KH 2 PO 4 , pH 7.2; Becton Dickinson Microbiology Systems), and then isolates were sonicated (40-Hz ultrasonic cleaner; VWR, Suwanee, GA) for 1 min to disperse aggregates. The suspensions were diluted 1:100 in Butterfield buffer for final test concentrations. Five milliliters of each suspension were placed into a small petri dish (50-mm diameter) along with a small sterile stir bar, and the petri dish was placed on a stir plate.UV irradiation was performed by using a collimated beam apparatus (Calgon Carbon, Pittsburgh, PA) equipped with a low-pressure lamp (254 nm) according to the standard method developed by Bolton and Linden (2). The surface of the suspension was placed 5 cm from the end of the collimating tube. The UV intensity was measured with a radiometer at 0.5-cm intervals across the test area and variability compensated for according to the UVCalc software directions (International UV association [http://www.iuva.org]). The fluences (UV doses) were determined using the UVCalc software, and the petri dishes were placed under the beam for at least five time periods to deliver a range of appropriate fluences to the organisms. Each irradiation test was conducted at ro...