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Applied and Environmental Microbiology, September 2001, p. 4382-4384, Vol. 67, No. 9
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.9.4382-4384.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Rapid Confirmation of Clostridium
perfringens by Using Chromogenic and Fluorogenic
Substrates
Philip W.
Adcock and
Christopher P.
Saint*
Microbiology Unit, Australian Water Quality
Centre, SA Water Corporation, Salisbury, South Australia 5108, Australia
Received 20 March 2001/Accepted 2 July 2001
 |
ABSTRACT |
The use of 4-methylumbelliferyl phosphate (MUP) and
ortho-nitrophenyl-
-D-galactopyranoside
(ONPG) for the identification of Clostridium perfringens
was investigated. A liquid assay containing both MUP and ONPG was a
highly specific alternative method for C. perfringens
confirmation, reducing incubation time from 48 to only 4 h. The
assay solution is easy to prepare, does not require anaerobic
conditions for use, and has an extended shelf life.
 |
TEXT |
The sulfite-reducing
clostridium group, including Clostridium perfringens, has
been shown to be of value in assessing fecal pollution of surface and
ground water (9) and estuarine (7) and
(10) ocean environments. C. perfringens is an
anaerobic, gram-positive, spore-forming bacillus that is capable of
surviving in soil and water for extended periods of time. Its presence
in the absence of other fecal indicators may reflect remote or
intermittent contamination in the distant past (9).
C. perfringens spores have been demonstrated to be useful
surrogate indicators for monitoring water treatment processes for the
removal of viruses (11), Giardia cysts, and
Cryptosporidium oocysts (11, 14). Their spores are similar in size to Cryptosporidium oocysts and have
similar chlorine resistance properties (11, 14). Although
primary isolation on tryptose sulfite cycloserine (TSC) agar takes
24 h, the standard method of confirmation for presumptive C. perfringens can take up to 72 h (1, 13). TSC
agar incorporates sodium metabisulfite and ferric ammonium citrate as
an indicator for sulfite reduction. Presumptive sulfite-reducing
clostridia, including C. perfringens, produce black
colonies. Isolates are subcultured onto blood agar (BA) for
aerotolerance testing, purity check, and Gram staining before
inoculation into nitrate motility medium (NMM) to detect nitrate
reduction and motility and into lactose gelatin medium (LGM) to detect
liquefaction of gelatin and lactose fermentation. Confirmation of
isolates is labor intensive, requires significant anaerobic workspace,
and is prone to misreporting of results due to the selection of mixed
cultures upon subculturing from TSC agar.
The detection of acid phosphatase has been shown to be a useful
diagnostic tool for identifying C. perfringens (4,
12). C. perfringens can metabolize
4-methylumbelliferyl phosphate (MUP) using the enzyme acid phosphatase
to produce 4-methylumbelliferone, which fluoresces when placed under
long-wavelength (365-nm) ultraviolet light. Additionally, C. perfringens ferments lactose to acid and gas, utilizing
-galactosidase in the process.
-Galactosidase activity has been
used successfully for the confirmation of coliforms by detecting
hydrolysis of
ortho-nitrophenyl-
-D-galactopyranoside (ONPG), which yields the chromogenic product
ortho-nitrophenol (6). We describe the
successful incorporation of MUP and ONPG into a liquid assay for
confirmation of C. perfringens, which we term the MUP-ONPG
assay. Compared to the standard technique, the MUP-ONPG assay
demonstrated superior sensitivity and specificity for the rapid
confirmation of C. perfringens.
Preparation of samples.
Water samples were collected for
processing from river, sewage effluent, and surface water storage
locations. Selection for sulfite-reducing clostridia including C. perfringens spores was undertaken by heat treatment of water
samples at 70°C for 20 min to kill vegetative cells. Heat-treated
samples were then filtered through a 0.45-µm-pore-size
cellulose-acetate membrane filter (Pall Gelman Corporation., Ann Arbor,
Mich.). Membranes were then transferred onto freshly prepared TSC or
TSC-MUP agar plates and incubated at 35°C for 24 h in an
anaerobic environment.
Media.
All chemicals were obtained from Sigma Chemical Company
(Sigma-Aldrich, St. Louis, Mo.) or BDH Laboratory Supplies Pty. Ltd. (Poole, Dorset, England). TSC agar and BA were prepared following the
manufacturer's recommendations (Oxoid Australia Pty. Ltd., Heidelberg,
Australia). NMM and LGM were prepared following recommended instructions (1, 13). TSC-MUP agar was prepared by adding MUP to molten (55°C) TSC agar to a final concentration of 85 mg/liter. The MUP-ONPG assay mixture was prepared by adding to 1 liter
of distilled water 5 g of ammonium sulfate, 10 g of sodium
chloride, 5.3 g of HEPES buffer sodium salt, 6.9 g of HEPES
buffer organic acid, 1 g of ONPG, and 0.15 g of MUP; the
final pH was 7.3 ± 0.1. Following filtration through a
0.2-µm-pore-size cellulose-acetate membrane filter (Pall Gelman),
100-µl aliquots were dispensed into sterile reaction tubes.
Inoculation and incubation of test media.
Anaerobic,
sulfite-reducing, gram-positive bacilli (presumptive C. perfringens) were purified on BA prior to inoculation into confirmatory media. All culture media were incubated at 35°C in an
anaerobic workstation (Don Whitley Scientific Pty. Ltd.,
Shipley, West Yorkshire, England) with a gas mixture of 10% hydrogen
in 90% nitrogen. TSC agar, TSC-MUP agar, and BA plates were incubated for 24 h; NMM and LGM inoculated culture media were incubated for
48 h. Isolates were inoculated into the MUP-ONPG mixture by rolling a sterile toothpick over the entire surface of an isolated colony and then emulsifying it in the mixture, ensuring that there was
sufficient inoculum to produce visible turbidity. The suspension was
then overlaid with sterile mineral oil to prevent evaporation. Tubes
were incubated in a heating block at 35°C for up to 24 h.
Biochemical tests.
Gram staining was performed following
standard procedures (5). Presumptive C. perfringens isolates, which produced discrepant results between
the standard and test confirmation methods, were identified using Vitek
anaerobic identification (ANI) cards following the manufacturer's
recommendations (Bio-Merieux, Marcy l'Etoile, France). Briefly, ANI
cards were inoculated with 1.8 ml of a 3 McFarland equivalence
turbidity standard of the test organism suspended in saline solution
(sodium chloride, 4.5 g/liter) and then incubated for 4 h at
35°C prior to reading of the results. These cards utilize 28 enzymatic tests, a Gram stain reaction, and an indole test to identify
anaerobic bacteria using a specially adapted database.
Reference cultures.
C. perfringens ATCC 13124 and
C. perfringens NCTC 8237 give positive results for all
C. perfringens confirmatory tests. Clostridium sporogenes ATCC 19404 gives positive results for sulfite reduction but is negative for the confirmation of C. perfringens.
TSC-MUP agar.
Initially we investigated the incorporation of
MUP into TSC agar as a possible way of combining primary isolation and
secondary confirmation of C. perfringens. In this trial, 30 river and surface water samples taken from locations known to be
impacted by fecal contamination were assessed. Samples were heat
treated and allowed to cool, and following filtration, membranes were
placed onto TSC-MUP agar. Plates were incubated anaerobically at 35°C
for 24 h. Fluorescence on TSC-MUP agar was difficult to interpret under UV due to diffusion of 4-methyl-umbelliferone, especially when
colonies were clustered together or when they were present in large
numbers. In some cases fluorescence appeared to be masked by
particulate matter. Subculturing of MUP-positive, presumptive C. perfringens isolates back onto TSC-MUP agar demonstrated that some
isolates failed to fluoresce when retested. Two such isolates were
identified as Clostridium bifermentans and Clostridium
subterminale using Vitek confirmation.
Due to the limitations of TSC-MUP agar for direct confirmation of
C. perfringens we tested the agar as an indirect
confirmation medium, whereby sulfite-reducing colonies arising on TSC
agar were confirmed by spot inoculation and incubation of TSC-MUP agar. A total of 224 presumptive C. perfringens isolates obtained
from 37 river and wastewater samples were transferred to TSC-MUP agar; 212 of 224 isolates fluoresced on TSC-MUP agar, whereas 169 of 224 were
confirmed by the standard confirmation technique. The data confirmed
that although TSC-MUP agar is sensitive (100%), it also has a high
false-positive rate (25.4%) when confirming C. perfringens,
with C. subterminale being the most common MUP-positive non-C. perfringens microorganism identified. An interesting
observation at this point was that the majority of C. perfringens isolates were positive for UV fluorescence within 4 to
6 h of TSC-MUP agar being inoculated.
MUP-ONPG assay.
As acid phosphatase activity alone was
unreliable for the confirmation of C. perfringens, a liquid
assay was developed which combined acid phosphatase detection with
-galactosidase activity in an attempt to improve specificity. MUP
and ONPG substrates were incorporated in HEPES buffer in the presence
or absence of 0.2% (wt/vol) sodium lauryl sulfate and 1% (wt/vol)
sodium chloride, concentrations which have previously been reported to
enhance
-galactosidase activity (3, 8).
Presumptive
C. perfringens isolates were emulsified in
MUP-ONPG reaction mixtures and then overlaid with sterile mineral oil
to eliminate evaporation. Reaction tubes including controls were
placed
in a heating block at 35°C and checked hourly over a 4-h
period, with
a final reading being taken at 24 h. The presence
of any yellowing
or fluorescence of the reaction mixture within
the 4-h period was
recorded as a positive result. Confirmation
of
C. perfringens using MUP-ONPG in HEPES buffer (pH 7.3) with
1%
(wt/vol) sodium chloride in the absence of lauryl sulfate showed
the
best correlation to the standard confirmatory technique, with
11 of 11 environmental isolates and both
C. perfringens control
strains being positive at 4 h. Importantly, in this assay
C. perfringens demonstrated acid phosphatase activity (UV
fluorescence) within
1 h and

-galactosidase activity (yellow
coloration) within 4
h.
The identities of 333 anaerobic, sulfite-reducing, gram-positive
isolates arising on TSC agar, which were from 40 wastewater
effluent,
10 river, and 18 surface water samples impacted by fecal
contamination,
were confirmed using the MUP-ONPG assay and the
standard method
(
1,
13). The MUP-ONPG mixture confirmed 164
of 333 isolates as
C. perfringens, compared to 153 of 333 using
the
standard method (Table
1). The 12 isolates negative by the
standard method that were positive using the
MUP-ONPG assay were
identified as
C. perfringens using Vitek
analysis. One isolate,
identified as
C. perfringens by
standard and Vitek analyses, demonstrated

-galactosidase activity
but failed to give significant acid phosphatase
activity within the 4-h
period. The MUP-ONPG assay demonstrated
a high level of sensitivity
(99.3%), although specificity (93.3%)
was adversely affected by the
number of false-negative results
(7.1%) obtained by the standard
method of confirmation. When two-sided
99% critical values were
applied using McNemar's test for agreement
(
2), no
significant disagreement (
P > 0.01) was detected.
Conclusion.
Direct isolation and confirmation of C. perfringens on TSC-MUP agar following membrane filtration was
unreliable due to diffusion of the UV fluorescent product
4-methylumbelliferone and interference from particulate matter.
Transfer of colonies from TSC agar to TSC-MUP agar for confirmation
gave a high false-positive rate, indicating that reliance on acid
phosphatase activity alone for confirmation is unreliable. Combining
detection of acid phosphatase and
-galactosidase activity using a
MUP-ONPG assay improved confirmation to a level superior to that of the
standard method, yielding results within 4 h. This test does not
need to be performed anaerobically, removing the need for prereduction
of media and complex anaerobic manipulations. Aliquots of the MUP-ONPG
mixture can be stored at
20°C for up to 3 months prior to use,
without loss of sensitivity. The method provides a convenient,
cost-effective, and rapid alternative to the standard method of
confirmation for C. perfringens.
 |
ACKNOWLEDGMENTS |
We thank the technical staff of the Microbiology Unit, Australian
Water Quality Centre, who contributed to this project and the staff of
the Microbiology Department, The Queen Elizabeth Hospital, Adelaide,
for assistance with specific bacterial identifications.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Australian Water
Quality Centre, SA Water Corporation, Private Mail Bag 3, Salisbury, South Australia 5108, Australia. Phone: 618 8259 0331. Fax: 618 8259 0228. E-mail: chris.saint{at}sawater.sa.gov.au.
 |
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Applied and Environmental Microbiology, September 2001, p. 4382-4384, Vol. 67, No. 9
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.9.4382-4384.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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(2009). Characterization of a Unique Class C Acid Phosphatase from Clostridium perfringens. Appl. Environ. Microbiol.
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