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Applied and Environmental Microbiology, July 2008, p. 4005-4011, Vol. 74, No. 13
0099-2240/08/$08.00+0 doi:10.1128/AEM.00417-08
Copyright © 2008, American Society for Microbiology. All Rights Reserved.
Occurrence and Genetic Diversity of Bacillus anthracis Strains Isolated in an Active Wool-Cleaning Factory
Pierre Wattiau,1*
Silke R. Klee,2
David Fretin,1
Mieke Van Hessche,1
Marie Ménart,1
Tatjana Franz,2
Camille Chasseur,3
Patrick Butaye,1 and
Hein Imberechts1
Department of Bacteriology and Immunology, Veterinary and Agrochemical Research Centre, Brussels, Belgium,1
Robert Koch-Institut, Centre for Biological Safety 2, Berlin, Germany,2
Section of Mycology, Scientific Institute of Public Health, Brussels, Belgium3
Received 19 February 2008/
Accepted 30 April 2008

ABSTRACT
Culturable microorganisms from various samples taken at an active
factory performing wool and goat hair cleaning were isolated
and analyzed.
Bacillus anthracis was found in air filter dust,
wastewater, and goat hairs, where it accounted for approximately
1% of the total counts of viable bacteria. Consistent with the
countries of origin of the processed material (South Caucasian
and Middle Eastern), all
B. anthracis isolates belonged to the
same phylogenetic cluster, as determined by variable-number
tandem repeat (VNTR) typing at eight loci. Within this cluster,
five closely related VNTR subtypes could be identified, of which
two were previously unreported. Additional diversity was observed
when more sensitive genetic markers were assayed, demonstrating
the multifocal nature of goat hair contamination. Goat hair
originating from areas where anthrax is endemic remains a material
with high biological risk for modern woolworkers.

INTRODUCTION
Bacillus anthracis is a gram-positive endospore-forming bacterium
that is capable of infecting both livestock and humans (
20).
Virulent strains of
B. anthracis cause disease by secreting
the lethal factor and edema factor toxins, together with a pore-forming
unit known as the protective antigen (
13,
21). Humans are infected
primarily through contact with products derived from contaminated
animals when contaminated material is ingested or inhaled or
comes into contact with an open wound (
1). Industrial anthrax,
also known as woolsorter's disease, was a serious threat in
the 19th and early 20th centuries, when the wool industry was
flourishing (
2). In Great Britain, substantial numbers of industrial
anthrax cases were reported for many years in western Yorkshire,
where most of the woolworking factories were clustered (
18).
The victims were not only woolworkers but also included people
and cattle that had been infected through the environmental
release of contaminated waste (
4). The concern was such that
the British government eventually voted in 1919 on the so-called
Anthrax Prevention Act, stating that any goods potentially contaminated
with anthrax must be disinfected upon entering United Kingdom
territory (
6). In the United States, apart from the 2001 attacks
(
17), the most recent anthrax epidemic was reported in 1957
in connection with a goat hair-processing mill in Manchester,
NH (
3). Today, the industrial processing of wool and goat hair
has almost disappeared from Western industrialized countries.
A very few factories exist, often in regions with historical
textile industries. In the European Community, where the import
of undisinfected wool is authorized, an industrial plant performing
middle-scale cleaning and disinfection of wool and goat hair
has been operating since 1890. In the present study, we investigated
the microbiological flora associated with hairs, dust, wastewater,
and sewage sludge at this plant, with a particular focus on
B. anthracis. Since goat hair and sheep wool are processed in
separate sections of the plant, the relative contamination of
each material was analyzed separately. Living anthrax spores
could be isolated only from goat hair, untreated wastewater,
and air dust collected from industrial filters. Forty-one
B. anthracis isolates selected at random were analyzed by two different
typing techniques (
8,
22). The results show that beyond apparent
relatedness, molecular diversity can be observed, demonstrating
the multiple origins of goat hair contamination.

MATERIALS AND METHODS
Sampling.
Samples were taken from materials representing different points
in the manufacturing process, namely, (i) gross hairs, (ii)
air dust, (iii) wastewater, and (iv) sewage sludge. Samples
of approximately 100 g of hairs were collected from the packed
bales and shaken overnight in 100 ml of phosphate-buffered saline
supplemented with 0.01% Triton X-100 (Sigma-Aldrich, St. Louis,
MO). The supernatant was concentrated into a final volume of
5 ml by centrifugation. For the analysis of industrial dust,
100-mg samples of material recovered from ventilation filters
were suspended in 10 ml of phosphate-buffered saline. Wastewater
and wet sewage sludge samples (1 g each) were analyzed as described
above.
Culture media and strain isolation.
Bacteria were routinely grown on sheep blood agar (Bio-Rad, La Jolla, CA) at 37°C. For enrichment with Bacillus strains, serial dilutions (500 µl each) of sampled material were plated onto polymyxin-lysozyme-EDTA-thallous acetate (PLET) medium (10). Environmental fungi were routinely grown for 5 days at 25°C on Bengal rose supplemented with chloramphenicol (100 µg ml–1). Thermoactinomycetes were isolated by incubating tryptic soy agar plates for 2 days at 52°C. Bacillus cereus ATCC 11778 and the vaccine strain B. anthracis Sterne were used for culture and PCR controls.
Air sampling and analysis.
Airborne particles were collected at the goat hair-loading place in the plant and counted. A control count of particles from another floor of the plant, where no industrial activity occurred, was performed simultaneously. APC Plus and RCS Plus devices (Biotest Hycon, Dreieich, Germany) were used for particle counting and direct inoculation of the particles onto specific solid media. An Airport MD8 device was used to collect air particles contained in 500-liter samples on circular gelatin filters that were subsequently deposited onto selective agar plates (Sartorius, Palaiseau, France).
Bacterial counting, identification, and typing.
Bacteria were identified by partial 16S rRNA gene sequencing as described previously (7). PCR primers and probes are listed in Table 1. The presence of typical anthrax virulence genes was investigated by two-color TaqMan real-time PCR performed with autoclaved, gross bacterial suspensions obtained by suspending PLET-grown colonies in 100 µl of 0.9% NaCl (wt/vol). A first PCR primer set (CAPC-F and CAPC-R) amplified a 96-bp fragment of capC, and a second pair (PAGA-F and PAGA-R) amplified a 97-bp portion of pagA. TaqMan probes (CAPC-1 and PAGA-1) labeled with a fluorophore at the 5' ends and the black hole quencher 1 at the 3' ends were used for real-time detection. These probes contained four internal locked nucleic acids each and hybridized to a target sequence in the amplified portions of capC and pagA. The capC and pagA primers and probes were designed with the software AlleleID (Premier Biosoft, Palo Alto, CA). Real-time PCR amplifications were conducted with a 25-µl volume containing premixed PCR reagents (ABgene, Epsom, United Kingdom) and each PCR primer at a 0.4 µM concentration. Double-dye probes were used at a 0.2 µM concentration. The following conditions were used for real-time PCR amplification on an IQ5 instrument (Bio-Rad, La Jolla, CA): 15 min at 95°C (1 cycle), followed by 20 s at 95°C, 30 s at 56°C, and 30 s at 72°C (45 cycles).
Variable-number tandem repeat (VNTR) typing was performed exactly
as described previously (
8), and the products were analyzed
by capillary electrophoresis on an ABI 3130XL genetic analyzer
(Applied Biosystems, Foster City, CA).
Single-nucleotide repeat (SNR) typing was conducted at four loci (CL7, CL10, CL12, and CL33) described by Stratilo et al. (22) by using four pairs of PCR primers. One primer in each pair was labeled with Cy5 at the 5' end. The nucleotide sequences of the SNR primers were as described by Stratilo et al. (22), except for one used for the amplification of locus CL10 (Table 1). For size analysis, 2 µl of a 50-fold dilution of the amplified PCR product was added to 38 µl of deionized formamide and 0.5 µl of DNA size standard 400 (Beckman Coulter, Fullerton, CA). Fragment analysis was conducted by capillary electrophoresis on a CEQ8000 instrument according to the instructions of the manufacturer (Beckman Coulter, Fullerton, CA).
Identification of fungi.
Fungi were identified according to macroscopic characteristics (colony aspects on specific agar media) and microscopic characteristics (mainly spore and conidiophore morphologies) (25).

RESULTS
The factory under investigation operates according to a rather
simple continuous process. Briefly, bales of packed wool or
goat hair are transferred from a storing area to a processing
area. Bales are opened, and their contents are loaded manually
onto a treadmill connected to a large mechanical shaker that
removes a substantial part of the mineral and organic material
attached to the fibers. The fibers are then transferred mechanically
to five successive washing tanks fed with freshwater by a counterflow.
Soaps, formaldehyde, and other cleaning substances are added
during the washing process according to proprietary procedures,
and the temperature is raised up to 50 to 55°C. The resulting
fibers, cleaned and disinfected, are eventually dried by being
heated at 80°C. Wastewater is purified at an on-site treatment
plant operating on the activated-sludge principle in open air.
The treated water is released into the municipal wastewater
treatment piping, and the residual sewage sludge is recycled
in different agricultural processes depending on its sanitary
quality.
In order to investigate the microbiological flora encountered in the factory, four different matrices were sampled and analyzed, namely, (i) hairs, (ii) air dust, (iii) wastewater, and (iv) sewage sludge. Since sheep wool and goat hair were processed at separate places in the plant, we concentrated on the goat hair section on the assumption that it had a greater chance of being contaminated by anthrax spores. Air dust samples were taken from collectors placed at the outlet of an industrial ventilation system running continuously during the processing whose inlets were connected to the treadmill-loading area and to the dry mechanical shaker. Wastewater was collected from the first washing tank, and sewage sludge was taken from the last decanter in the treatment plant.
Microbiological analysis.
A representative dust sample taken during the processing of goat hair was investigated for its microbiological content. Total viable bacteria were isolated on either rich medium (blood agar) or selective medium for Bacillus (PLET) (10), and partial 16S rRNA gene sequencing was conducted for 41 colonies picked at random. Table 2 shows that Bacillus was by far the dominating genus. Macrococcus caseolyticus was isolated occasionally on blood agar, whereas Enterococcus, Vagococcus, and Wautersiella species were enriched together with Bacillus on the selective PLET medium. Hairs, dust, and wastewater taken from the first washing tank turned out to display similar bacterial contents. The fungal content of the same dust sample was analyzed in detail. As shown in Table 3, Penicillium and Aspergillus were the dominating genera, accounting for 30 and 20% of the total fungal load, respectively. Cladosporium, Alternaria, Ulocladium, Scopulariopsis, and Fusarium species were found in limited quantities, while thermoactinomycetes (Thermoactinomyces candidus) represented up to 7% of the total culturable fungi. The occasional occurrence of opportunistic pathogens or mycotoxin-producing molds (11), such as Aspergillus fumigatus, Cladosporium cladosporioides, and Alternaria and Ulocladium species, was noticed.
B. anthracis identification tests were performed systematically
on any CFU growing on PLET medium. The isolation of
B. anthracis from hairs was difficult due to the large amount of fibers required
(a minimum of 100 g), which rendered the handling of the fibers
in common laboratory vessels arduous. Dust and wastewater samples
were much more convenient to handle and were used to isolate
a representative pool of
B. anthracis strains. Heating the samples
for 10 min at 85°C did not affect the number of
B. anthracis CFU significantly, suggesting that mainly the sporulated form
accounted for goat hair contamination. All
B. anthracis strains
were nonhemolytic on sheep blood agar and contained both pXO1
and pXO2 plasmids as assessed by real-time PCR. Repeated attempts
to isolate
B. anthracis from sewage sludge were unsuccessful.
As shown in Table
4,
B. anthracis could be retrieved from samples
derived from the processing of goat hair but not of sheep wool.
Besides differences in the bacterial loads due to the way the
animals are farmed, the origins of the tested material (European
sheep wool versus Eastern goat hair) are the most probable explanation
for the observed
B. anthracis counts.
Air-suspended-particle counts.
In order to get a picture of the microbiological load in the
factory air, air particles were collected during the processing
of a representative goat hair batch and counted. Figure
1 shows
that the number of 5-µm particles in the treadmill-loading
area increased by about 2 orders of magnitude upon the start
of processing and reached a maximum of 25,000 per liter of air
after 2 h of processing. The increase in 1-µm particles
was less substantial (from 6,000 to 45,000 particles liter
–1 on average), while the number of 0.3-µm particles remained
stable, in the range of 100,000 particles liter
–1. A slight
increase in 1- and 5-µm particles was observed in a control
area located on another floor of the factory, suggesting that
the process induced a global increase in particle counts inside
the whole factory. Total particles from 500-liter air samples
were suspended in physiological water, and serial dilutions
were plated onto either rich or selective medium. Total counts
of viable organisms did not exceed 25 CFU liter
–1, meaning
that just 1 of 3,000 particles of 1 µm or more was culturable.
As observed during dust and wastewater analysis,
B. anthracis bacteria represented about 1% of the total counts of viable
organisms and were never detected at a concentration higher
than 1 CFU in 5 liters of air.
VNTR and SNR typing.
VNTR analysis of 41
B. anthracis isolates was conducted according
to the method of Keim et al. (
8), which involves eight genetic
markers. Table
5 shows that all 41 isolates belonged to VNTR
cluster A4. Five closely related genotypes differing at only
two VNTR loci were identified, of which two (those of strains
40 and 41) were so far unreported. Genotype 71 was by far the
most abundant and accounted for 88% of the total isolates. Indigenous
Belgian strains causing natural anthrax in cows some 30 years
ago were included in the study to further ascertain the exogenous
nature of the
B. anthracis spores contaminating the factory.
As expected, these strains displayed VNTR genotypes unrelated
to those of goat hair isolates, ruling out any possible contamination
from the outdoor environment. More sensitive markers of the
SNR type were assessed for all strains as well. From the 29
SNR markers for
B. anthracis described previously (
22), 4 were
chosen for their presumptive variability among strains of the
A4 VNTR cluster. Of these four markers, three exhibited substantial
variability and demonstrated further diversity among the goat
hair isolates, as evidenced by the eight different SNR subtypes
(numbered 71-A through 71-H in Table
5) observed for strains
matching VNTR genotype 71.

DISCUSSION
Industrial anthrax was a threat for woolworkers in Western countries
until the second half of the 20th century. Scientific investigations
conducted during the 1957 U.S. epidemic in Manchester, NH, led
to the conclusion that the processing of goat hairs, especially
carding and combing, posed a very high risk and prompted the
authorities to close down the incriminated mill (
3,
5). The
finding of
B. anthracis in a Belgian factory raised an opportunity
to reinvestigate the issues some 50 years later with modern
methods for microorganism characterization and airborne-particle
analysis. The present article reports the microbiological results
of this investigation. Epidemiological assessment and occupational
medicine aspects will be reported elsewhere.
Our study confirmed the presence of anthrax spores in goat hair originating from South Caucasian and Middle Eastern countries, where anthrax is endemic. The contamination of goat hair by anthrax spores is thus an ongoing problem and should in no way be underestimated as far as biosafety and health protection are concerned. The counting and analysis of airborne spores revealed concentration peaks in the range of 1 B. anthracis spore in 5 liters of air, which is close to the rates observed in the Manchester mill in 1957 (5). The area in the Belgian factory highly loaded with dust was, however, just transiently so; it is much smaller than the 1800 m2 of the Manchester mill's card-comb area (3), and it is equipped with air extractors. Moreover, the woolworkers now wear protective equipment. The factory employs fewer personnel than the Manchester mill, about 70 people compared to the 600 Manchester employees. These noticeable differences, together with the overall moderate incidence of industrial anthrax (1.5 cases per 100 employees for the 1957 epidemic), probably account for the lack of a single industrial anthrax case report from the Belgian factory over its 120 years of activity.
The genetic typing of 41 B. anthracis isolates selected at random showed that they all belonged to the same phylogenetic cluster, A4, defined by Keim et al. (8) and matched one major and four minor genotypes within this cluster. This genotyping method uses an eight-locus VNTR typing scheme which has been shown previously to display valuable and consistent subspecies typing capacities worldwide, in spite of the highly monomorphic character of the B. anthracis genome. However, the discriminative power of these markers becomes limited when faced with strains of close geographical origins, as exemplified in the present study and elsewhere (16). In such contexts, diversity can be demonstrated only if a larger number of VNTR markers (12, 15) are analyzed or if more sensitive markers (9, 14, 19, 22-24) are assessed. In the present study, we chose to analyze four markers of the SNR type, of which three exhibited substantial diversity when the goat hair isolates were assayed and allowed no fewer than 12 subtypes to be defined (22). It is hence very unlikely that hair bale contamination issued from just one carrier animal or from one herd of carrier goats; rather, it likely originated from many carriers which had been exposed to multiple endemic foci. The tentative assignment of particular B. anthracis genotypes to countries of origin was complicated by the fact that hairs of different origins and colors are mixed together at the start of processing to meet customers' quality requirements. At best, B. anthracis strains isolated directly from packed hairs may be considered to be representative of a country. This association could be illustrated for just two strains isolated from Russian and Afghan batches but could not be assessed consistently due to the difficulty and poor yield of B. anthracis isolation from this material.
Four Belgian indigenous strains of B. anthracis were included in the genotyping study to ascertain the external origins of the strains isolated in the factory. As expected, these indigenous strains displayed genotypes unrelated to the goat hair strains, with two of them matching VNTR cluster A3.b and the remaining two matching cluster B1. Thus, the indigenous strains were clearly unrelated to the strains retrieved from imported goat hair, all of which matched cluster A4. From a general point of view, it is surprising to observe more intrinsic diversity at the VNTR level among strains originating from the small territory of Belgium than among strains issuing from large countries in the Middle East. Whether the latter are representative of the global B. anthracis diversity in the Middle East or reflect goat carriage only or whether the differences in diversity result from the higher-level resistance of sporulated B. anthracis strains belonging to cluster A4 is a question raised by this study that would deserve further investigation in the future.
The occurrence of opportunistic pathogens or mycotoxin-producing fungi, such as Aspergillus fumigatus, Cladosporium cladosporioides, and Alternaria and Ulocladium species in the form of airborne spores, in the manufacture should also be considered a risk for the woolworkers' health since these organisms are known to induce or exacerbate allergic reactions and may cause respiratory diseases (11).
Attempts to isolate B. anthracis from materials derived from sheep wool processing in the investigated factory were unsuccessful, probably due to the origin of the sheep wool in countries where anthrax is not considered to be endemic. An analysis of sludge material sampled at the on-site treatment plant revealed no anthrax contamination within the detection limits of the methodology used. Chemicals such as formaldehyde added during hair processing, as well as heating and the inhibitory effect of and competition from the activated-sludge organisms, are likely to account for B. anthracis clearance from the treated wastewater. The present study thus also validated the efficiency of the disinfection process and of the activated-sludge treatment applied to the factory's wastewater for the removal of anthrax spores. Waste controls should be conducted regularly, however, to ensure the safe and permanent removal of such high-threat contaminants.

ACKNOWLEDGMENTS
We thank the manager and employees of the wool-processing plant
for their courtesy and collaboration and M. Govaerts (Veterinary
and Agrochemical Research Centre) and B. China and G. Hanquet
(Scientific Institute of Public Health), as well as Y. Pirenne
(chief medical inspector) and M. Poncin and J. M. Henkinbrant
(occupational medicine), for helpful discussions. Special thanks
to E. Kissling (Scientific Institute of Public Health) for critical
reading of the manuscript and to J. Tesch (Robert Koch-Institut)
for expert technical assistance.

FOOTNOTES
* Corresponding author. Mailing address: Veterinary and Agrochemical Research Centre, Department of Bacteriology and Immunology, Groeselenberg 99, B-1180 Brussels, Belgium. Phone: 32 (0)2 3790426. Fax: 32 (0)2 3790670. E-mail:
Pierre.Wattiau{at}var.fgov.be 
Published ahead of print on 16 May 2008. 

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Applied and Environmental Microbiology, July 2008, p. 4005-4011, Vol. 74, No. 13
0099-2240/08/$08.00+0 doi:10.1128/AEM.00417-08
Copyright © 2008, American Society for Microbiology. All Rights Reserved.