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Applied and Environmental Microbiology, December 2003, p. 7216-7223, Vol. 69, No. 12
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.12.7216-7223.2003
Copyright © 2003, American
Society for
Microbiology. All Rights Reserved.
Diversity of Bacteria Associated with Natural Aphid Populations
S. Haynes,1,
A. C. Darby,1,
T. J. Daniell,2 G. Webster,3,
F. J. F. van Veen,4 H.C.J. Godfray,4 J. I. Prosser,3 and A. E. Douglas1*
Department of Biology, University of York, York YO10 5YW,1
NERC Centre for Population Biology, Imperial College at Silwood Park, Ascot SL5 7PY, England,4
Plant-Soil Interactions, Scottish Crop Research Institute, Invergowrie, Dundee DD2 5DA,2
Department of Molecular and Cell Biology, University of Aberdeen Institute of Medical Sciences, Foresterhill, Aberdeen AB25 2ZD,Scotland3
Received 6 June 2003/
Accepted 22 September 2003

ABSTRACT
The
bacterial communities of aphids were investigated by terminal
restriction
fragment length polymorphism and denaturing gradient gel
electrophoresis
analysis of 16S rRNA gene fragments generated by PCR
with general
eubacterial primers. By both methods, the

-proteobacterium
Buchnera was detected in
laboratory cultures of six parthenogenetic lines
of the pea aphid
Acyrthosiphon pisum and one line of the black
bean aphid
Aphis fabae, and one or more of four previously described
bacterial
taxa were also detected in all aphid lines except one of
A. pisum. These latter bacteria, collectively
known as secondary
symbionts or accessory bacteria, comprised three
taxa of

-proteobacteria
(R-type [PASS], T-type
[PABS], and U-type [PAUS]) and a rickettsia
(S-type
[PAR]). Complementary analysis of aphids from natural
populations
of four aphid species (
A. pisum [
n
= 74],
Amphorophora rubi [
n
= 109],
Aphis sarothamni [
n
= 42], and
Microlophium carnosum [
n
= 101]) from a single geographical location revealed
Buchnera and up to three taxa of accessory bacteria, but no
other bacterial
taxa, in each aphid. The prevalence of accessory
bacterial taxa
varied significantly among aphid species but not with
the sampling
month (between June and August 2000). These results
indicate
that the accessory bacterial taxa are distributed across
multiple
aphid species, although with variable prevalence, and that
laboratory
culture does not generally result in a shift in the
bacterial
community in aphids. Both the transmission patterns of the
accessory
bacteria between individual aphids and their impact on aphid
fitness
are suggested to influence the prevalence of accessory
bacterial
taxa in natural aphid
populations.

INTRODUCTION
Many symbioses between animals and microorganisms are traditionally
described
as binary associations, i.e., relationships between an animal
and
single taxon of symbiotic microorganism
(
16). However, it is
becoming
increasingly apparent that this perspective is an
oversimplification
because animals generally harbor multiple microbial
taxa (
24,
26).
This shift in focus
can be illustrated by the microbial symbiosis
in aphids. Until
recently, virtually all research on the microbial
symbiosis in aphids
has concerned the

-proteobacterium assigned
to the genus
Buchnera, which accounts for >90% of the
microbial
cells in aphids
(
2,
15).
Buchnera
cells are restricted to specific
aphid cells (known as bacteriocytes)
in the insect body cavity,
are obligately vertically transmitted, and
are required by the
insect for normal growth and reproduction
(
5,
15,
17). However,
many aphids
additionally harbor one to several other bacterial
taxa, known as
secondary symbionts or accessory bacteria, including
taxa known
informally as R-type (PASS), S-type (PAR), T-type
(PABS) and U-type
(PAUS). The accessory bacterial taxa generally
have a broader tissue
distribution in aphids than
Buchnera does
and can be
transmitted among aphids both vertically and horizontally
(
6,
7,
8,
11,
17,
20,
34,
35).
The pea aphid,
Acyrthosiphon pisum, has also been reported to
bear
Spiroplasma
(
21),
Erwinia
(
23), and
Staphylococcus
(
3,
22)
spp.
A key
feature of the accessory bacterial taxa in aphids is that, unlike
Buchnera, they are not generally universal in any one aphid
species (8,
11,
12,
20,
34,
35). In principle, the
distribution of accessory bacteria can be accounted for by the
occasional horizontal acquisition and failure of vertical transmission,
perhaps compounded by selection for or against insects containing the
accessory bacteria. It has been suggested that the accessory bacteria
may be transmitted horizontally by the oral route (i.e., feeding from
plants contaminated with these bacteria) or by aborted parasitoid
attack (i.e., attack by a parasitoid whose ovipositor has become
contaminated by a previous attack of an aphid harboring the accessory
bacterium) (13,
35). There is evidence
that the accessory bacteria may have positive, negative, or no effect
on aphid fitness, depending among the bacterial taxa and with
environmental conditions
(8,
12,
18,
30). However, a general
limitation to these considerations is that much of the research to date
on the interactions between aphids and accessory bacteria has been
conducted on aphids in long-term laboratory culture. The bacterial
diversity of some insects is altered by laboratory maintenance
conditions (14,
27), and the possibility
cannot be excluded that the microbial taxa of aphids are similarly
changed or reduced by laboratory conditions.
The core purpose of
this study was to investigate the microbiota of aphids by two PCR-based
methods, terminal restriction fragment length polymorphism (T-RFLP) and
denaturing gradient gel electrophoresis (DGGE) analysis of amplified
16S rRNA gene fragments, both of which have been used widely for the
analysis of microbial communities. These approaches have the advantage
over the methods previously used to study accessory bacteria in aphids
(sequencing of clonal libraries, taxon-specific PCR assays) that they
offer rapid and robust assays of bacterial taxa, whether or not they
have been found previously in aphids
(29,
32,
33). These methods are
therefore well suited to studying the bacterial communities in natural
aphid populations and particularly to investigating whether the
bacterial community differed substantially between aphids from natural
populations and in long-term laboratory
culture.

MATERIALS AND
METHODS
Aphids.
Three classes of aphid material were
used: DNA from five reference
lines of
Acyrthosiphon pisum
with known bacterial community
profiles as determined by 16S rRNA gene
library sequencing,
taxon-specific PCR, and in situ hybridization
analysis (Table
1);
two parthenogenetic lines of aphids,
A. pisum JF98/24 and
Aphis fabae HR91/3, in long-term culture on
Vicia
faba cv. The Sutton;
and field samples of four species, collected
from a damp meadow
at Silwood Park, Berkshire, United Kingdom, between
June and
August 2000:
A. pisum and
Aphis sarothamni
from
Cytisus scoparius,
Amphorophora rubi from
Rubus fruticosus, and
Microlophium carnosum from
Urtica dioica. DNA was extracted from single aphids by
using
the DNeasy tissue kit (Qiagen) as specified by the manufacturer.
Fresh
material was used for the laboratory lines, and aphids
from natural
populations were transferred directly from the
host plant to individual
tubes of acetone (
19) and
stored at
room temperature until DNA was extracted up to a year
later.
T-RFLP analysis.
16S rRNA gene fragments were
amplified from total aphid DNA
by using the general bacterial primers
Y2MOD (5'-ACT-YCT-ACG-GRA-GGC-AGC-AGT-RGG-3')
(
Escherichia coli positions 338 to 361), modified
from that described in
reference
43 and labeled at the
5' end with the phosphoramidite
dye 6-FAM (MWG Biotech UK,
Milton Keynes, United Kingdom), and
16SB1 (
E. coli positions
1491 to 1512) (
6), by 24
cycles of
94°C for 1 min, 54°C for 1 min, and
72°C for 1 min,
but with the extension time increased to 2 min
for the first
and last cycles. The amplification reaction mixtures
contained
20 mM Tris-HCl (pH 8.4), 50 mM KCl, 2 mM MgCl
2,
100 µM
each deoxynucleoside triphosphate (Promega), each primer
at
0.2 µM, and 1 U of Platinum
Taq polymerase (Gibco,
Life
Technologies) in 50-µl volumes. This followed preliminary
experiments
that (i), revealed that a greater diversity of 16S rRNA
gene
amplification products was obtained consistently with Platinum
Taq polymerase than with other enzymes tested and (ii),
optimized
the PCR conditions by a Taguchi approach
(
10). A sample of the
PCR
product from each amplification was run on a 1.5% agarose
gel,
the remainder of the sample was purified with the Qiaquick
PCR
purification kit (Qiagen) as specified by the manufacturer,
and
subsamples (15 µl) were digested either with 3 U of
AluI
and 2.5 U of
BseR1 (New England Biolabs)
(37°C for 2 h)
(AB digestion) or sequentially with 3
U of
SmaI (25°C for
2 h) followed by 3 U of
ClaI and 3 U of
XbaI (37°C for 2
h)
(Promega) (SCX digestion). A 2-µl volume of each restriction
digest
was mixed with 1 µl of GS500 size standard (Applied
Biosystems)
and run on a 4.5% polyacrylamide gel on an ABI 377
automated
sequencer. The results were analyzed using Genescan version
2.02
(Applied Biosystems). Table
2 shows the predicted restriction
sites for each of the five enzymes
used, together with the 5'-terminal
restriction fragments
(5'-T-RFs), for bacteria previously reported
in aphids and for
E. coli,
Staphylococcus, and
Wolbachia. The
restriction
enzymes were selected from inspection of 5'-T-RF
patterns for
a variety of enzymes, initially in silico using the
Ribosomal
Database Project (RDP) database to construct T-RF outputs and
subsequently
in test experiments that checked the reproducibility of
the
method. With the restriction enzymes selected (but not some
other
apparently suitable enzyme combinations), the detected
complement of
bacteria did not differ among multiple amplifications
from the same DNA
templates or with 1:10 dilutions of the template,
and the observed
positions of the peaks in the electropherograms
were ±1 bp from
the predicted positions.
DGGE
analysis.
A 16S rRNA gene
fragment of ca. 200 bp was amplified with the
general bacterial 16S
rRNA gene primers P2 and P3 (
E. coli positions
341 to 357 and
518 to 534, respectively)
(
32) from a template
of
total aphid DNA or in a nested PCR amplification using as
template the
products of a PCR amplification with primer pair
16SA1 and 16SB1
(
E. coli positions 8 to 27 and 1491 to 1512,
respectively)
(
6). All amplifications
were performed in 50-µl
volumes under the conditions given in
reference
32. PCR
products
were checked by agarose gel electrophoresis (2%
[wt/vol] agarose)
and stained with ethidium bromide prior to
DGGE analysis. DGGE
was carried out as described previously
(
37,
41). PCR products
(ca.
200 ng of each product) were separated using gradient polyacrylamide
gels
(6 to 12% [wt/vol] polyacrylamide) with a
denaturing gradient
between 40 and 60% (100% denaturing
conditions are 7 M urea
and 40% [vol/vol] formamide).
Gels were poured with the aid
of a 50-ml volume gradient mixer (Fisher
Scientific, Loughborough,
United Kingdom), and electrophoresis was done
at 75 V for 16
h at 60°C. The polyacrylamide gels
were visualized under
UV following staining with ethidium bromide. All
bands were
excised, homogenized in 10 µl of sterile distilled
water,
and incubated at 4°C overnight. The sample (1
µl)
was then reamplified by PCR (as above) and used as a
template
for a direct sequencing reaction with the BIG-Dye sequencing
kit
(Applied Biosystems) with the P3 primer. The partial 16S rRNA
gene
sequences obtained were analyzed for DNA sequence similarity
using the
BLASTN algorithm (
1) to
the search the online GenBank
DNA database. All sequences were checked
for chimeric artifacts
by using the CHECK_CHIMERA program of
RDP
(
28).

RESULTS
Evaluation
of methods for bacterial community analysis.
The T-RFLP electropherograms obtained
from the PCR amplifications
of the five reference lines of aphids are
shown in Fig.
1A to
J.
They show the peaks conforming to the predicted T-RF of
Buchnera and accessory bacterial taxa previously identified in
each line
(Tables
1 and
2). Peaks predicted for
other bacterial taxa previously
found in aphids (Table
2) were not detected in
any electropherograms.
Additional peaks in some samples from all
lines were detected
at 163 and 172 bp for the AB digestion and 72, 80,
and 88 bp
for the SCX digestion (Fig.
1). Supplementary
experiments (data
not shown) revealed these peaks in digestions with
different
restriction enzymes and in undigested controls, suggesting
that
they were PCR artifacts, such as fluorescently labeled concatemers
of
primer-dimers and misprimed products. Aphid line IS also generated
a
peak at 313 bp (Fig.
1E),
and some AB electropherograms of
all lines included a broad peak at
>500 bp. These peaks were
interpreted as partial digestion
products: 313 bp of R-type
bacteria and >500 bp of all
amplicons (
Buchnera and R-, T-,
and U- type bacteria have an
AluI restriction site at ca. 520
bp [Table
2]). Complete
digestion could not be achieved by extending
the incubation time
because the manufacturer recommends that
the enzyme
BseRI not
be used in digestion reactions longer than
2 h. The partial
digestion product of R-type bacteria at 313
bp in the AB T-RF could be
used to identify R-type bacteria
in samples that additionally bore
T-type bacteria. This overcame
a limitation of the protocol, which in
principle can discriminate
R-type and T-type bacteria in single
infections only, because
both bacteria have a T-RF at 122 bp in the AB
profile and T-type
bacteria have a T-RF at 323 bp in the SCX digestion
(Table
2).
(The
theoretical T-RF of
E. coli is also at 313 bp, but
E.
coli and R-type bacteria can be discriminated in the SCX T-RF
profile
[Table
2]). The broad peak
at >500 bp attributed to partial
digestion products of various
bacterial 16S rRNA gene fragments
masked the predicted T-RF of
Spiroplasma, and it was concluded
that
Spiroplasma
could not be identified reliably by the T-RFLP
protocol.
The
T-RFLP electropherograms of the two laboratory lines A. pisum
JF98/24 and Aphis fabae HR91/3 contained peaks attributable to
Buchnera and U-type bacteria.
The DGGE profiles of the
200-bp 16S rRNA gene fragment amplified from the five reference lines
and two laboratory lines of A. pisum yielded one to four bands
(Fig.
2a). One band in each profile was identified by sequencing as an amplicon
from Buchnera (Table
3); the Buchnera band in Aphis fabae HR91/3 was markedly
less mobile within the DGGE gel than in the A. pisum lines,
indicating that the sequence of the amplicons differed between
Aphis fabae and A. pisum. The accessory bacteria
identified in each aphid line by DGGE matched the results from the
T-RFLP analysis precisely. However, two bands in the profile for line
IS were assigned to R-type bacteria and two bands in line R were
assigned to S-type bacteria, indicative of microdiversity in both of
these accessory bacterial taxa detectable by DGGE but not by T-RFLP
(Fig. 2a; Table
3). Many of the reactions
also yielded a band with slightly greater mobility than the
Buchnera fragment (e.g., the bands labeled
"artifact" for lines LMB95/28, IS, JF98/24, and HR91/3
in Fig. 2a). The sequences
of the band at this position varied between reactions and, when checked
for chimeras, were found to include Buchnera sequence and a
region(s) of low homology to other
-proteobacteria
sequences, whose identity varied among samples. When these sequences
were included in phylogenetic analyses, they disrupted the tree
topology by forming an unsupported outgroup clade (<50%)
to the Buchnera sequences (data not shown). This type of tree
disruption is characteristic of chimeric artifacts
(25).
View this table:
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TABLE 3. Similarities
of sequences of 16S rRNA gene fragments derived from DGGE bands to
reference database sequences
|
Bacterial
community in aphids from natural populations.
The T-RFLP electropherograms of all 324
aphids scored included
a peak identical to the predicted T-RF of
Buchnera, and many
also had peaks that could be assigned to
the R-, S-, T-, and
U-type accessory bacteria. In addition, some
A.
pisum individuals
(but none of the other three aphid species) that
generated a
122-bp peak in the AB T-RF profile (Fig.
1K), as expected for
R-type
and T-type bacteria, had a previously undescribed peak at 316
bp
after SCX digestion (Fig.
1L). DGGE analysis of
these aphids
yielded two bands. One band had the mobility
characteristic
of the
Buchnera product, and the other band
could be assigned
to R-type bacteria on the basis of its sequence (Fig.
2; Table
3).
In other words, the
SCX T-RF of 316 bp could be attributed to
a variant of R-type bacteria
with a
XbaI restriction site at
316 bp downstream of the
5' end of the amplicon. Among the 72
individuals of
A.
pisum tested, 38 bore R-type bacteria with
the standard T-RF
profile and 46 bore the "variant" R-type bacteria
with
a
XbaI restriction site at 316 bp.
The number of
different bacterial taxa detected in the natural populations of four
aphid species is summarized in Table
4. No individual aphid harbored more than three taxa of accessory
bacteria, and the number of bacterial taxa per aphid varied
significantly among the aphid species (Kruskall-Wallis test: H
= 226.73, 3 degrees of freedom [df], P
< 0.001), from 94% of Amphorophora rubi,
which harbored no accessory bacteria, to 69% of
Microlophium carnosum with two accessory bacterial taxa. The
distribution of different accessory bacterial taxa is shown in Table
5. T-type was the only accessory bacterium detected in at least one
individual of all four aphid species, harbored by 57% of
Aphis sarothamni individuals and <10% of the
other aphid species. Between 93 and 94% of both Microlophium
carnosum and A. pisum had R-type. The U-type was rarely
detected as the sole accessory bacterium: of the 84 aphids bearing
U-type bacteria, 82 (all but two Microlophium carnosum
individuals) also had R-type or T-type bacteria. The S-type was rare,
detected in just 3 (<1%) of the 324 aphids scored. The
frequency of accessory bacteria in A. pisum and Aphis
sarothamni, the two aphid species with the same host plant,
Cytisus scoparius, was significantly different
(
2 = 79.01, 2 df, P <
0.001; S-type bacteria excluded from analysis).
The data sets for
all aphid species except
Amphorophora rubi were suitable for
analysis of the variation in the frequency
of accessory bacteria with
month of collection. For each aphid
species, seasonal variation was not
statistically significant
(Table
6).
None of the T-RFLP electropherograms of the 324 aphids from
natural
populations yielded the expected T-RFs for
Erwinia or
Staphylococcus sp., bacteria previously found in aphids in
laboratory culture
(
3,
22,
23).

DISCUSSION
The
concordance between the bacterial taxa identified by DGGE
and T-RFLP
was excellent for the reference lines (aphids with
previously described
accessory bacterial complements), laboratory
lines, and aphids from
natural populations. All aphids were
confirmed to have a low apparent
diversity of bacteria, with
no more than four taxa (
Buchnera
and three taxa of accessory
bacteria) in any individual aphid (Table
4). The possibility
should
not be excluded, however, that aphids may harbor additional
bacterial
taxa that yield poor or no 16S rRNA gene PCR amplification
products
with the methods used as a result of PCR primer bias
or low template
abundance (
38,
40).
This study
additionally identified sequence microdiversity from analysis of the
length of the 5'-TF in the T-RFLP electropherograms of R-type
bacteria in A. pisum (Fig. 1K
and L) from natural populations and from the different DGGE
migration patterns for both R-type and S-type bacteria in the reference
lines of A. pisum (Fig.
2; Table
3). Such heterogeneity
could limit the applicability of the currently used diagnostic PCR
assays, which generally have been designed on the basis of a few
uniform sequences. For example, the R-type sequences obtained from
amplicons used in DGGE analysis included sequence variation within a
widely used taxon-specific primer, PASSF
(7,
8,
30), but the impact of
this variation on the reliability of the R-type-specific assay remains
to be established. Variation in both 16S rRNA gene sequence between
bacterial cells (36) and
between multiple gene copies within single bacterial cells, as occurs
in some but not all bacterial taxa
(4,
9,
31), may contribute to
this observed heterogeneity. The importance of multiple gene copies
could be investigated by fluorescent in situ hybridization studies
using probes which target the variable sites. This microheterogeneity,
together with the similar mobility of the amplicons of different
accessory bacteria in DGGE (Fig.
2), requires that DGGE
bands be analyzed further by sequencing or Southern blotting for
bacterial taxa to be identified, and this can limit the usefulness of
DGGE as a rapid screen for bacterial communities in aphids.
Two
principal conclusions can be drawn from this study of the bacterial
community in aphids. First, the similarity of bacterial taxa identified
in the aphid samples from long-term laboratory cultures and natural
populations indicates that laboratory culture, which is known to affect
the microbiota of some insects (see introduction), does not generally
result in a substantial shift or reduction in the microbial community
in aphids. In general terms, this conclusion confirms the relevance of
laboratory-based studies of the aphid-microbe interactions (see, e.g.,
references 8 and
13). Exceptionally,
however, Erwinia and Staphylococcus spp. have been
found previously in laboratory cultures of A. pisum
(3,
22,
23) but were not detected
in the aphids (including six A. pisum lines from long-term
laboratory culture) studied here. Further research is required to
establish whether this discrepancy reflects a susceptibility of aphids
in laboratory culture to occasional colonization by bacteria not
representative of natural populations or limitations of the molecular
assays, perhaps linked to poor template availability or PCR bias
(38,
40). The results of the
T-RFLP analysis are, however, consistent with the report
(42) that
Wolbachia is apparently absent from aphids.
The second
conclusion is that the four taxa of accessory bacteria initially
identified in A. pisum
(6,
7,
11,
35) occur in multiple
aphid species but that none of these taxa was universally present, at
least for the natural populations of the four aphid species
investigated here. This conclusion confirms and extends published data
sets obtained for one to several individuals of multiple aphid species
by using taxon-specific PCR assays
(34,
35), although the
accessory bacteria referred to as V, So-So and Ars types in reference
34 were not detected in
any aphids studied here. Horizontal transmission between aphid species
is expected to contribute to the distribution of accessory bacteria
because the phylogeny of accessory bacteria in different aphid species
is not congruent with the phylogeny of their aphid partners
(34,
35). Therefore, aphids
generally can be considered a "habitat" for the
accessory bacteria. These bacterial taxa have not, to date, been found
under the free-living conditions, raising the possibility that aphids,
and possibly other insects
(11,
34), are essential for
the long-term persistence of these bacteria.
Immediately arising
from these considerations are questions about the processes underlying
the observed interspecific variation in frequency of aphids bearing the
various accessory bacteria. In addition to stochastic effects,
contributory factors may include differences in the capacity of
different accessory bacterial taxa to colonize and persist in the
various aphid species and effects of the bacteria on aphid fitness.
Three comparisons suggest that the impact of these factors may vary
with bacterial taxon and environmental circumstance. First,
experimental manipulations indicate that A. kondoi is
incompatible with R-type bacteria from A. pisum
(8) but that Aphis
fabae is fully compatible with T-type bacteria from A.
pisum (13). Second,
a study of the significance of temperature as a determinant of the
incidence of accessory bacteria has linked the elevated incidence of
aphids bearing R-type bacteria in natural populations experiencing high
temperatures in California to enhanced tolerance of high temperature in
A. pisum harboring this bacterial taxon in the laboratory
(30). However, no
significant between-month variation in the frequency of accessory
bacteria in British aphid populations was found either in the aphid
species examined in this study (Table
6) or for T-type bacteria
in A. pisum
(12). This difference may
reflect the more equable climate in the United Kingdom than in
California. Finally, the host plant has also been implicated as an
important correlate of the accessory bacterial complement in A.
pisum (8). For
example, individuals of A. pisum affiliated with
Trifolium (clover) species tend to harbor U-type bacteria
(39). However, the
significantly different bacterial complements of A. pisum and
Aphis sarothamni on Cytisus scoparius (Table
5) indicate that this link
between plant and accessory bacterial complement does not necessarily
extend to members of different aphid species.
In summary, the
application of community-based molecular methods in this study to
investigate the microbiota of aphids has provided the basis to explore
the ecology of accessory bacterial taxa. The two chief issues to
resolve are the habitat range of accessory bacteria, including the
significance of aphids to their persistence, and the factors
determining the incidence of accessory bacteria in aphids, predicted to
include both transmission patterns and the impact of accessory bacteria
on aphid fitness. The ecology of the various accessory bacterial taxa
is not thought to be uniform; studies of these bacterial taxa offer the
opportunity to explore the range of strategies available to
nonpathogenic microorganisms associated with
animals.

ACKNOWLEDGMENTS
We thank C. Montllor and T.
Fukatsu, who provided us with the
aphid DNA for reference lines, and J.
Ferrari, who provided
us with aphid line JF98/24.
This study was
funded by NERC grants NER/B/S/2000/00054 and
GST/01/1837.

FOOTNOTES
* Corresponding author. Mailing address: Department of Biology, University of York, P.O. Box 373, York YO10 5YW, England. Phone: 44-1904-328610. Fax: 44-1904-432860. E-mail:
aed2{at}york.ac.uk.

Present address: Department of Biomolecular Sciences, UMIST, Manchester M60 IQD, England. 
Present address: Centre for Tropical Veterinary Medicine, The University of Edinburgh, Easter Bush Veterinary Centre, Roslin EH25 9RG, Scotland. 
Present address: Cardiff School of Biosciences, Cardiff University, Cardiff CF10 3TL, Wales. 

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Society for
Microbiology. All Rights Reserved.
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