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Applied and Environmental Microbiology, February 2003, p. 1327-1330, Vol. 69, No. 2
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.2.1327-1330.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
UV Resistance of Bacillus anthracis Spores Revisited: Validation of Bacillus subtilis Spores as UV Surrogates for Spores of B. anthracis Sterne
Wayne L. Nicholson* and Belinda Galeano
Department of Veterinary Science and Microbiology, University of Arizona, Tucson, Arizona 85721
Received 25 July 2002/
Accepted 30 October 2002

ABSTRACT
Recent bioterrorism concerns have prompted renewed efforts towards
understanding the biology of bacterial spore resistance to radiation
with a special emphasis on the spores of
Bacillus anthracis. A review of the literature revealed that
B. anthracis Sterne
spores may be three to four times more resistant to 254-nm-wavelength
UV than are spores of commonly used indicator strains of
Bacillus subtilis. To test this notion,
B. anthracis Sterne spores were
purified and their UV inactivation kinetics were determined
in parallel with those of the spores of two indicator strains
of
B. subtilis, strains WN624 and ATCC 6633. When prepared and
assayed under identical conditions, the spores of all three
strains exhibited essentially identical UV inactivation kinetics.
The data indicate that standard UV treatments that are effective
against
B. subtilis spores are likely also sufficient to inactivate
B. anthracis spores and that the spores of standard
B. subtilis strains could reliably be used as a biodosimetry model for the
UV inactivation of
B. anthracis spores.

INTRODUCTION
The October 2001 bioterrorist attack with
Bacillus anthracis spores has sparked renewed interest in studying methods of bacterial
spore inactivation and the mechanisms by which spores resist
the lethal effects of various disinfection treatments. UV radiation
at a 254-nm wavelength has been used as an efficient and cost-effective
means of disinfecting surfaces (
1,
4,
15,
16,
17), building
air (
3,
8,
13), and drinking water supplies (
5). The most reliable
method for testing the efficacy of UV disinfection equipment
is biodosimetry, the use of a test organism to measure the biologically
effective UV dose (
2). Commonly used test organisms for UV biodosimetry
studies are bacterial spores, usually spores of
Bacillus subtilis,
due to their high degree of UV resistance, reproducible inactivation
response, and ease of use (reviewed in references
9 and
11).
In particular, exhaustive testing of spores of the
B. subtilis strain ATCC 6633 has resulted in this strain serving as the
current European biodosimetry standard for 254-nm UV disinfection
of drinking water (
5).
Semilogarithmic plots of spore inactivation versus UV fluence (dose) produce a characteristic curve, consisting of a shoulder at low UV doses, followed by a curve reflecting exponential inactivation at higher UV doses (Fig. 1). Two parameters often used to describe spore resistance to UV are (i) the UV dose lethal for 90% of the population (LD90) and (ii) the decimal reduction value (D value), defined as the UV dose which reduces spore viability by a factor of 10, measured from the exponential portion of the inactivation curve (6, 11). For example, from the published data of Hoyer (5) (Fig. 1), it can be calculated that spores of B. subtilis ATCC 6633 exhibit an LD90 and a D value of 260 and 120 J/m2, respectively (Table 1).
In stark contrast to the extensively characterized UV inactivation
response of
B. subtilis spores, much less work has been performed
to characterize the UV inactivation kinetics of
B. anthracis spores. Perhaps the most complete work was a study which examined
UV resistance of spores of the attenuated
B. anthracis Sterne
animal vaccine strain (
7). From examination of the data presented
in that report (
7), we calculated that the
B. anthracis Sterne
spores exhibited LD
90 and
D values of 810 and 540 J/m
2, respectively
(Table
1). Taken at face value, these data might be cause for
concern, as they would suggest that
B. anthracis Sterne spores
are three to four times more resistant to 254-nm UV than are
B. subtilis spores, and hence they may not be efficiently inactivated
by standard UV disinfection treatments. However, the apparent
UV inactivation response of a spore population can vary considerably,
depending on the growth and sporulation environment and the
methods used for spore purification, irradiation, and UV dosimetry
(
2,
5,
10). For this reason, the use of values from different
studies to make comparisons of spore resistance to UV between
different species is not valid. The most reliable method for
testing intrinsic differences in spore resistance to UV between
strains is to assay all strains in parallel, under identical
conditions of growth, sporulation, spore purification, irradiation,
dosimetry, and survival determination. In this article, we report
that, when all such experimental variables were controlled,
B. anthracis Sterne spores exhibited UV inactivation kinetics
that were essentially indistinguishable from those of the spores
of standard
B. subtilis biodosimetry strains.
The bacterial strains used in this study were B. subtilis strain WN624 (amyE::spc), an isogenic derivative of the standard laboratory strain 168; B. subtilis strain ATCC 6633, provided by David Battigelli and available from the American Type Culture Collection (ATCC; Manassas, Va.); and B. anthracis Sterne, available from the Colorado Serum Company (Denver, Colo.). All of the bacteria were sporulated by incubation in liquid Schaeffer's sporulation medium (SSM) (14) at 37°C for 48 h with vigorous aeration in a rotary shaker. The cultures were harvested by centrifugation (5,000 x g, 10 min, 25°C), and the spores were purified by using the lysozyme and buffer-washing method described by Nicholson and Setlow (12), heat shocked (80°C, 10 min), and stored in deionized water at 4°C. The viable titers of all spore preparations were determined by serial 10-fold dilution in phosphate-buffered saline (PBS; 10 mM potassium phosphate, 150 mM NaCl, pH 7.4) and plating on SSM solidified with 1.7% agar.
UV irradiation was performed by using a commercial low-pressure mercury vapor lamp (model UVGL-25; UV Products, Upland, Calif.) with the filter removed, producing predominantly 254-nm-wavelength UV radiation. Throughout the experiments, the lamp was placed at a constant height of 42 cm above the target. The UV output was measured with a UVX radiometer fitted with a UVX-25 filter (UV Products), which was recently calibrated and traceable to the National Institute of Standards and Technology standard. Before the experiments were performed, UV fluence rates were measured at 0.5-cm intervals from the center of the target area along both the x and y axes, the values obtained were entered into UVCalc (a Microsoft Excel program developed by James Bolton and posted on the website of the International UV Association [http://www.iuva.org]), and the relative UV fluence rate pattern throughout the target area was computed. Once the relative UV intensity pattern was obtained, the UV fluence rate at the center of the target was measured before each experiment and entered into UVCalc to obtain the average UV fluence rate over the surface of the target for each experiment. Purified spores were diluted to a final concentration of 106/ml in 10 ml of PBS. The absorbance at 254 nm (A254) of the resulting spore suspension was determined in a Beckman DU-6 UV/visible spectrophotometer, and the results were entered into UVCalc. Factors accounting for reflectance and depth of the spore suspension were also entered into UVCalc. The resulting exposure times needed for the desired UV doses were computed. The spore suspension was pipetted into the bottom of an uncovered 6-cm-diameter petri dish, a sterile stir bar was added, the dish was placed on a magnetic stir plate, and the samples were removed from the suspension at UV doses of 0, 100, 200, 400, and 600 J/m2. The samples were serially diluted 10-fold in PBS, plated in duplicate on solid SSM, and incubated at 37°C for 48 h, and the resulting colonies were counted. The surviving fraction of spores was calculated by dividing the viable spore titer at any given UV dose (S) by the spore titer obtained from the nonirradiated suspension (S0). Each irradiation experiment was repeated four times, and the averages and standard deviations of each set of data points were calculated by using Minitab version 10.5 software.
The UV inactivation curves obtained from the spores of B. subtilis ATCC 6633, B. subtilis WN624, and B. anthracis Sterne are presented in Fig. 1. For purposes of visual comparison of results among strains, we superimposed our inactivation curves onto the UV inactivation curve of the European standard biodosimetry strain ATCC 6633 that was reported by Hoyer (5) (Fig. 1). In our hands, the UV inactivation curves of the B. subtilis ATCC 6633 spores were very similar among the four replicate experiments and very closely matched the published data (5) (Fig. 1A), indicating that our spore purification and UV dosimetry protocols are highly reproducible, both in repeated trials in our laboratory and between our laboratory and that of Hoyer (5). The UV inactivation curve of our wild-type UV biodosimetry strain, B. subtilis WN624, also closely matched that of B. subtilis ATCC 6633 and exhibited high reproducibility among the four replicated experiments (Fig. 1B). The UV inactivation curve of the B. anthracis Sterne spores (Fig. 1C) differed slightly from that of the B. subtilis standard in exhibiting a slightly more pronounced shoulder at UV doses of 0 to 200 J/m2 and a slight tail at UV doses between 400 and 600 J/m2. These differences were minor, and overall the B. anthracis inactivation curve closely matched those obtained with the B. subtilis ATCC 6633 and WN624 spores. From the UV inactivation curves for all three spore types, we calculated the LD90 and D values for comparison with the literature values (Table 1). Under our experimental conditions, the B. anthracis Sterne spores exhibited LD90 and D values of 275 and 140 J/m2, respectively, which are very close to the values computed for B. subtilis spores under the same controlled conditions (Table 1) and which are certainly not three to four times greater as previously reported (7).
As discussed above, some of the experimental factors which can lead to considerable variation in the apparent resistance of bacterial spores to UV are (i) the method of spore preparation, (ii) the irradiation conditions, and (iii) the dosimetry method used. We examined these factors in order to better understand how they influence the apparent UV resistance of a spore population.

Spore preparation.
In an earlier benchmark study (
7), spores were prepared by growing
B. anthracis Sterne for 3 to 4 days on a blood agar plate, washing
the harvested cells twice in sterile distilled water, and treating
them with heat (60°C, 30 min). When we prepared
B. anthracis Sterne spores by this method, we noted that sporulation did
not occur at a high frequency, the majority of the cells present
in the final suspension had not sporulated, and the few spores
formed were often not completely liberated from the characteristic
chains in which they had developed (Fig.
2). This situation
could lead to an overestimate of
B. anthracis spore resistance
to UV for two reasons. First, 1 CFU can consist of multiple
spores, all of which must be UV inactivated in order to result
in the destruction of that particular CFU, thus leading to an
artificial inflation of the apparent UV resistance. We also
noted that spores were not completely liberated from spore chains
when we allowed
B. anthracis Sterne to sporulate in liquid SSM
(data not shown). To correct for this, we subjected our
B. anthracis Sterne spore preparations to further purification by lysozyme
treatment and a series of buffer and detergent washes (
12).
Microscopic examination of the final spore suspension after
further purification revealed that the spores had been liberated
from chains and that the amount of nonsporulated cells and other
debris had been reduced substantially (Fig.
2B).

Irradiation conditions.
In the earlier benchmark study,
B. anthracis Sterne spores were
resuspended in phenolized gel-phosphate buffer (28 mM sodium
phosphate, dibasic; 0.2% gelatin; 1% phenol [pH 7.2] [
7a]) and
UV irradiated at a relatively high density of spores (2
x 10
7 CFU/ml) (
7). These conditions could lead to an artificial overestimate
of the spore resistance to UV due to absorption of UV by the
gelatin and phenol in the buffer and shielding by the additional
turbidity provided by nonsporulated cells as discussed above
(Fig.
2A). In the present work, spores were irradiated at a
20-fold-lower density (10
6/ml), at which no visible turbidity
was evident and which resulted in low
A254 values of the spore
suspensions (0.022 ± 0.0093). Further, to take even these
low
A254 values into account, a correction factor for
A254 of
the suspension was programmed into UVCalc. This is an important
consideration, as discussed below.

UV dosimetry.
In the benchmark study (
7), UV fluence at the surface of the
suspension was correctly measured with a commercial UV meter
but no correction was made for the shielding by nonsporulated
cells, absorption of UV by the resuspension medium itself, or
the depth of the suspension. These general considerations have
recently been addressed by James Bolton, who developed UVCalc,
a Microsoft Excel spreadsheet designed to take these factors
into account in calculations of the biologically effective UV
fluence in aqueous suspensions. In order to determine the extent
to which the turbidity of, and absorbance of UV by, the phenolized
gel-phosphate buffer affects the apparent UV resistance of
B. anthracis Sterne spores, we undertook the following experiment.
B. anthracis Sterne spores were prepared as described elsewhere
(
7) by growth on blood agar plates and resuspension in phenolized
gel-phosphate buffer, diluted to 3
x 10
5 CFU/ml in PBS, and
UV irradiated. The UV fluences used were calculated by using
UVCalc with (i) no correction factor, (ii) correction for the
A254 value of the buffer, and (iii) correction for the
A254 values of both the buffer and the spore suspension. The results
of this experiment (Fig.
3) strongly support the notion that
UV absorption by the buffer and by the turbid suspension leads
to an overestimate of the apparent spore resistance to UV. Indeed,
when these factors are taken into account, it appears that
B. anthracis Sterne spores prepared from blood agar plates (Fig.
3) may be slightly less UV resistant than comparable spores
prepared by growth in SSM (Fig.
1C).
In conclusion, to establish unambiguously the level of UV resistance
of
B. anthracis Sterne spores, we prepared, purified, and assayed
the resistance of the spores in parallel with spores of standard
B. subtilis biodosimetry strains whose UV-inactivation characteristics
are well established. When all of the variables associated with
spore production, purification, irradiation, and UV dosimetry
were accounted for, we found that
B. anthracis Sterne spores
exhibited essentially the same resistance to 254-nm-wavelength
UV as do spores of standard, currently available UV biodosimetry
strains of
B. subtilis. Therefore, in the absence of evidence
that spores of virulent
B. anthracis strains are more UV resistant
than are
B. anthracis Sterne, we conclude that
B. subtilis spores
can serve as safe and accurate substitutes for
B. anthracis spores in validating the efficacy of 254-nm-wavelength UV-disinfection
devices.

ACKNOWLEDGMENTS
We thank Gregory Knudson for helpful discussion, David Battigelli
for providing us with
B. subtilis ATCC 6633, and James Bolton
for generously providing UVCalc to the scientific community.
This work was supported in part by a grant from the Arizona Agriculture Experiment Station (USDA Hatch) to W.L.N.

FOOTNOTES
* Corresponding author. Mailing address: Department of Veterinary Science and Microbiology, Building 90, Room 102, University of Arizona, Tucson, AZ 85721. Phone: (520) 621-2157. Fax: (520) 621-6366. E-mail:
WLN{at}u.arizona.edu.


REFERENCES
1 - Banrud, H., and J. Moan. 1999. The use of short wave ultraviolet radiation for disinfection in operating rooms. Tidsskr. Nor. Laegeforen. 119:2670-2673.[Medline]
2 - Bolton, J. R. 2000. Terms and definitions in ultraviolet disinfection, 1-16. In Proceedings of "Disinfection 2000." Water Environment Federation, Alexandria, Va. .
3 - Cundith, C. J., C. R. Kerth, W. R. Jones, T. A. McCaskey, and D. L. Kuhlers. 2002. Air-cleaning system effectiveness for control of airborne microbes in a meat-processing plant. J. Food Sci. 67:1170-1174.[CrossRef]
4 - Gardner, D. W. M., and G. Shama. 1998. The kinetics of Bacillus subtilis spore inactivation on filter paper by u.v. light and u.v. light in combination with hydrogen peroxide. J. Appl. Microbiol. 84:633-641.[CrossRef]
5 - Hoyer, O. 2000. The status of UV technology in Europe. IUVA News 2:22-27.
6 - Joslyn, L. 1983. Sterilization by heat, p. 3-46. In S. S. Block (ed.), Disinfection, sterilization, and preservation. Lea & Febiger Publishers, Philadelphia, Pa.
7 - Knudson, G. B. 1986. Photoreactivation of ultraviolet-irradiated, plasmid-bearing, and plasmid-free strains of Bacillus anthracis. Appl. Environ. Microbiol. 52:444-449.[Abstract/Free Full Text]
7 - Little, S. F., and G. B. Knudson. 1986. Comparative efficacy of Bacillus anthracis live spore vaccine and protective antigen vaccine against anthrax in the guinea pig. Infect. Immun. 52:509-512.[Abstract/Free Full Text]
8 - Nakamura, H. 1987. Sterilization efficacy of UV irradiation on microbial aerosols under dynamic airflow by experimental air conditioning systems. Bull. Tokyo Med. Dent. Univ. 34:25-40.[Medline]
9 - Nicholson, W. L., and P. Fajardo-Cavazos. 1997. DNA repair and the ultraviolet radiation resistance of bacterial spores: from the laboratory to the environment. Recent Res. Dev. Microbiol. 1:125-140.
10 - Nicholson, W. L., and J. F. Law. 1999. Method for purification of bacterial endospores from soils: UV resistance of natural Sonoran desert soil populations of Bacillus spp. with reference to B. subtilis 168. J. Microbiol. Methods 35:13-21.[CrossRef][Medline]
11 - Nicholson, W. L., N. Munakata, G. Horneck, H. J. Melosh, and P. Setlow. 2000. Resistance of Bacillus endospores to extreme terrestrial and extraterrestrial environments. Microbiol. Mol. Biol. Rev. 64:548-572.[Abstract/Free Full Text]
12 - Nicholson, W. L., and P. Setlow. 1990. Sporulation, germination, and outgrowth, p. 391-450. In C. R. Harwood and S. M. Cutting (ed.), Molecular biological methods for Bacillus. John Wiley & Sons, Sussex, England.
13 - Riley, R. L. 1994. Ultraviolet air disinfection: rationale for whole building irradiation. Infect. Control Hosp. Epidemiol. 15:324-325.[Medline]
14 - Schaeffer, P., J. Millet, and J.-P. Aubert. 1965. Catabolic repression of bacterial sporulation. Proc. Natl. Acad. Sci. USA 54:704-711.[Free Full Text]
15 - Stannard, C. J., J. S. Abbiss, and J. M. Wood. 1985. Efficiency of treatments involving UV irradiation for decontaminating packaging board of different surface compositions. J. Food Prot. 48:786-789.
16 - Stermer, R. A., M. Lasater-Smith, and C. F. Brasington. 1987. UV radiation, an effective bactericide for fresh meat. J. Food Prot. 50:108-111.
17 - Volpon, A. G. T., C. A. Elias, and A. Drozdowicz. 1990. An efficient device for sterilizing irregular surfaces. J. Microbiol. Methods 11:51-58.
Applied and Environmental Microbiology, February 2003, p. 1327-1330, Vol. 69, No. 2
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.2.1327-1330.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
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