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Applied and Environmental Microbiology, September 2000, p. 3883-3890, Vol. 66, No. 9
Freshwater Biological
Association1 and Institute of Freshwater
Ecology,4 Far Sawrey, Ambleside, Cumbria LA22
OLP, United Kingdom; Laboratorium voor Microbiologie,
Universiteit Ghent, B-9000 Ghent, Belgium2; and
Fish Disease Laboratory, Department of Microbiology, National
University of Ireland, Galway, Republic of
Ireland3
Received 16 March 2000/Accepted 4 July 2000
Oxytetracycline-resistant (OTr) mesophilic aeromonads
were recovered from untreated hospital effluent (72 isolates) and from fish farm hatchery tanks (91 isolates) at sites within the English Lake
District, Cumbria, England. The transfer of OTr plasmids
from these isolates was investigated. Using Escherichia coli J53-1 as a recipient, 11 isolates from the hospital site and
6 isolates from the fish farm site transferred OTr plasmids
(designated pFBAOT1 to 17). Original isolates were identified using
fatty acid methyl ester and fluorescent amplified fragment length
polymorphism comparisons as either Aeromonas hydrophila HG3
(eight isolates), A. veronii b.v. sobria HG8 (six
isolates), and A. caviae HGB5 (one isolate). One isolate
remained unidentified, and one could not be assigned a taxonomic
designation beyond the genus level. Plasmids pFBAOT1 to -17 were
screened for the presence of the tetracycline resistance determinants
Tet A to E and Tet G. Only determinant Tet A (10 plasmids) was detected
in these plasmids, with 7 tet gene determinants remaining
unclassified. In all cases, Tet A was located on a 5.5-kb
EcoRI restriction fragment. Hybridization with
inc-rep probes N, P, Q, W, and U showed pFBAOT3, -4, -5, -6, -7, -9, and -11, from the hospital environment, to be IncU
plasmids. Further, restriction fragment length polymorphism (RFLP)
analyses and DNA probing demonstrated that pFBAOT plasmids were closely
related to IncU OTr plasmids pASOT, pASOT2, pASOT3, pRAS1
(originally isolated from A. salmonicida strains from fish
farms in Scotland and Norway, respectively), and pIE420 (isolated from
a German hospital E. coli strain). In addition, DNA
analyses demonstrated that plasmids pRAS1 and pIE420 had identical RFLP
profiles and that all fragments hybridized to each other. The presence
of tetracycline resistance transposon Tn1721 in its
entirety or in a truncated form in these plasmids was demonstrated.
These results provided direct evidence that related tetracycline
resistance-encoding plasmids have disseminated between different
Aeromonas species and E. coli and between the human and aquaculture environments in distinct geographical locations. Collectively, these findings provide evidence to support the hypothesis that the aquaculture and human compartments of the environment behave
as a single interactive compartment.
Members of the genus
Aeromonas are ubiquitous in most aquatic environments
(19). Several species have been implicated in fish disease
(e.g., Aeromonas hydrophila, A. sobria, A. allosaccharophila, A. salmonicida, and A. veronii; 6), and pathogenicity in humans has
been demonstrated by A. hydrophila, A. veronii,
A. jandaei, A. trota, and A. schubertii (23). Treatment or prevention of disease in
both humans and fish has been undertaken extensively using
antimicrobial agents. It has been estimated that the total amount of
antibiotics used in aquaculture and agricultural practices is
approximately equal to that employed in the therapy of human disease
(46), as typified by Norway in 1989 (14). This
has resulted in an increase in the frequency of bacteria resistant to
these agents to the extent that they may affect the treatment of human
and fish diseases, in addition to impacting the aquaculture environment
directly (40). It was concluded that there was inadequate information to allow a quantitative or even a qualitative assessment of
the risk to human health posed by antimicrobial agent usage (28,
40). Smith et al. (40) suggested that the greatest potential risk was presented by the transfer of plasmid-encoded resistance genes between the aquatic compartment and the human compartment of the environment. Furthermore, they identified our lack
of understanding of the survival of bacterium-plasmid complexes in the
environment as the major limitation in our knowledge (40).
Tetracyclines (TCs) have been used exclusively in aquaculture,
particularly to control furunculosis in salmonids (40).
Inevitably, resistance to oxytetracycline (OT) and TC emerged and was
found to be plasmid encoded (1, 37, 38). The frequency of
resistance to TCs in A. salmonicida has increased with
greater usage from 4% of isolates from 1979 to 1981 (4) to
greater than 50% of isolates examined from Scottish fish farms in the
early 1990s (34). Assessing the extent of antibiotic
resistance in bacterial isolates presents many difficulties (25,
26). Adams and coworkers (1) recognized that there was
a need to assess the true nature of OTr at the molecular
level. Their strain set contained 66% of isolates with transferable
OTr which was subsequently shown to be encoded by large
plasmids (the pASOT group) that carried a 5.4-kb EcoRI
restriction fragment containing the Tet A determinant (1).
The detection of OTr bacteria in the aquaculture industry
showed that this environment, like hospitals, was facing a threat from
the use of antibiotics (1). Their study also highlighted the
need to extend the investigation to isolates from other geographical
locations and to other fish pathogens (1). Furthermore, they
suggested that the ability of plasmids to spread among the bacterial
population present in, and beyond, fish farm environments should be
investigated (1).
In this study, we have assessed whether there is sufficient evidence to
suggest that the aquaculture and human environments exist as two
separate entities with distinct transfer events or whether they
comprise a single interactive compartment of the environment where free
exchange of genetic information occurs. To test these hypotheses, we
investigated the dissemination of conjugative OTr plasmids
between isolates in the human and aquaculture compartments of the
environments using OTr mesophilic aeromonads recovered from
untreated hospital effluent and from a fish farm facility as model
organisms and environments.
Bacterial strains, plasmids, and sampling.
The bacterial
strains and plasmids used in this study are described in Table
1. Escherichia coli strains
and Pseudomonas putida PaW340 (a derivative of P. putida nt-2) were maintained on Iso-Sensitest agar (ISA; Oxoid,
Basingstoke, United Kingdom). All OTr control strains were
maintained on ISA supplemented with OT-HCl (25 µg ml
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Distribution of Oxytetracycline Resistance Plasmids
between Aeromonads in Hospital and Aquaculture Environments:
Implication of Tn1721 in Dissemination of the
Tetracycline Resistance Determinant Tet A
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ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results and Discussion
References
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results and Discussion
References
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials and Methods
Results and Discussion
References
1)
obtained from Vetrapharm (Hampshire, United Kingdom).
TABLE 1.
Strains and plasmids used in this study
1) and incubated at
28 ± 0.5°C for 24 h. OTr was confirmed by
streaking five randomly selected presumptive aeromonads from each
bottle onto ISA supplemented with OT (25 µg ml
1) and
incubation at 28°C for 24 h. One of the five confirmed isolates was then maintained for further study.
Antibiotic susceptibility testing. Susceptibility of aeromonad field isolates and transconjugants to the antibiotics AP (25 µg), OT (30 µg), TC (30 µg), streptomycin (SM; 10 and 30 µg), nalidixic acid (NA; 30 µg), rifampin (RD; 25 µg), kanamycin (KM; 30 µg), and trimethoprim (TM; 5 µg) was assessed on ISA in accordance with the established Kirby-Bauer procedure (7) using disks supplied by Oxoid.
Identification of isolates. All isolates were initially confirmed as Aeromonas spp. at the genus level by PCR amplification of the aroA gene as described previously (42). Further characterization was carried out by gas-liquid chromatographic analysis of cellular fatty acid methyl esters using the Microbial Identification System (Microbial ID Inc.) as previously described (22). The resulting fatty acid methyl ester patterns were identified automatically and compared with the database AER48C (20) for the identification of mesophilic aeromonads. Isolates that could not be unambiguously classified into one of the known Aeromonas DNA hybridization groups (HGs) or genomic species by comparison with the AER48C database were subjected to whole-genome analysis with the fluorescent amplified fragment length polymorphism analysis technique as described previously (21). Digitized fluorescent amplified fragment length polymorphism fingerprints were further processed using the GelCompar software package (Applied Maths) and compared for identification with the laboratory database AEROLIB (21).
Conjugation experiments.
Filter matings were performed by
separately resuspending a loopful of freshly cultured donor and
recipient cells in 300 µl of 1× phosphate-buffered saline (pH 7.4)
(36), followed by overlaying 10 µl of each suspension onto
a 0.22-µm-pore-size membrane filter (Supor-200; Gelman) and then
incubation at 28 ± 0.5°C for 24 h. Controls (unmixed
donors and recipient cells) were treated in the same manner. After
incubation, cells and controls were resuspended in 450 µl of
phosphate-buffered saline and transconjugants were selected by
spreading onto either ISA supplemented with OT (25 µg
ml
1) and RD (50 µg ml
1) at 37°C for
24 h (when E. coli J53-1 was used as the recipient) or
ISA supplemented with OT (25 µg ml
1) and SM (500 µg
ml
1) for 24 h at 30°C (when P. putida
was the recipient). E. coli J53-1 transconjugants were
confirmed by demonstration of OT and RD resistance phenotypes and
auxotrophy for proline and methionine. P. putida
transconjugants were confirmed by OT and SM resistance and auxotrophy
for tryptophan.
DNA manipulations.
Restriction endonuclease digestion and
agarose gel electrophoresis were carried out using established
techniques (36). Plasmid DNA was extracted from control
strains and E. coli J53-1 transconjugants after growth in
Luria-Bertani medium supplemented with OT (25 µg ml
1)
at 37°C with shaking at 150 rpm for 18 h using Qiagen mini and midi columns or using the sucrose gradient plasmid extraction technique
(47).
Construction and labeling of DNA probes.
DNA probes for the
determinants Tet B and Tet D were constructed as previously described
(31) and were purified using GenElute agarose gel
purification spin columns (Supelco). Probes for the determinants Tet A,
Tet C, Tet E, and Tet G were created via PCR using primers specific to
these determinants in accordance with an established protocol
(15). PCR probes were purified using the Nucleon QC
PCR/oligo clean up kit (Amersham-Pharmacia Biotech). Probes specific to
Tn1722 and the methyl-accepting chemotaxis protein
(MCP)-encoding gene of Tn1721 were constructed from pMT1286 (45). The entire Tn1722 region was produced by
digesting pMT1286 with EcoRI and excision and purification
of the 5.6-kb fragment. The MCP probe was prepared by digestion of
pMT1286 with EcoRI and HindIII to produce a
fragment of 1.2 kb. Excised DNA was purified using the Qiaex II DNA
purification kit (Qiagen). DNA probes were labeled with
[
-32P]dCTP as specified in the random-primed
hexanucleotide labeling kit (Roche-Molecular Biochemicals).
DNA blotting and hybridizations.
In all cases, DNA was
blotted onto positively charged nylon membrane (Roche-Molecular
Biology). Southern transfers (43) were carried out in
accordance with standard procedures (36) using 0.4 M NaOH as
the transfer, denaturation, and fixation buffer. Dot blots were
performed with QIAGEN plasmid DNA (denatured at 95°C for 10 min), and
the DNA was fixed with UV light (302 nm) for 3 min. Prehybridization
was carried out in prewarmed (68°C) 5× SSPE (1× SSPE is 0.18 M
NaCl, 10 mM NaH2PO4, and 1 mM EDTA [pH 7.7])
containing 5× Denhardt's solution, 0.5% (wt/vol) sodium dodecyl
sulfate (SDS), and 0.25% (wt/vol) N-lauryl sarcosine for 5 to 6 h. Hybridization was performed in fresh prewarmed solution (prehybridization solution without the addition of Denhardt's solution) at 68°C for 18 to 20 h. Unbound radioactive probe DNA was removed by washing membranes twice for 10 min (each time) in 2×
SSPE-0.1% (wt/vol) SDS at room temperature (20 to 25°C), followed
by 15 min at 68°C in 1× SSPE-0.1% (wt/vol) SDS and two washes of
15 min (each) in 0.1× SSPE-0.1% (wt/vol) SDS at 68°C. The
membranes were then wrapped in cling film and exposed to X-ray film
(Hyperfilm-MP; Amersham-Pharmacia) at
70°C for up to 3 days.
Cloning.
Plasmid DNA was cloned into pUC18
(Amersham-Pharmacia-Biotech) in accordance with standard procedures
(36). Transformation was carried out using E. coli DH5
competent cells in accordance with the methodology of
the supplier (Clontech).
DNA sequencing and analyses. Cloned DNA was partially sequenced using the universal forward and reverse primers homologous with pUC18 using an ABI Prism 373 sequencer. FASTA and BLAST DNA homology searches were performed using the programs within the DNA Data Bank of Japan (DDBJ) at the following internet address: http://www.ddbj.nig.ac.jp/E-mail/homology.html.
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RESULTS AND DISCUSSION |
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Isolation of OTr aeromonads and conjugation experiments. A total of 163 presumptive OTr mesophilic aeromonads were isolated from the hospital (72 isolates) and fish farm (91 isolates) sample sites. All isolates were assessed for susceptibility to the antibiotics TC, OT, RD, SM, NA, and KM using sensitivity test disks. All isolates were confirmed as resistant to TC and OT. The most common resistance observed in both environmental groups was to NA (94% of isolates from the hospital and 52% of isolates from the fish farm), while 14% of hospital isolates and 40% of the fish farm isolates were resistant to SM. Resistance to both NA and SM was observed in isolates from both environments. A total of 90% of those isolates that were SM resistant, and 13% of the NA-resistant isolates from the hospital were resistant to both antibiotics, while 75% of SM-resistant and 57% of NA-resistant isolates from the fish farm were resistant to both. No isolates were RD or KM resistant.
The susceptibility of all of the isolates to RD permitted the use of E. coli J53-1 (plasmid free, RD-resistant, and OTs) as a recipient strain in conjugation experiments. Conjugation experiments involving all of the isolates and E. coli J53-1 were carried out, and 17 transconjugants demonstrating the correct phenotype (11 from the hospital and 6 from the fish farm) were obtained. Agarose gel electrophoresis showed that for each transconjugant, only one plasmid was transferred (data not shown). The plasmids were designated pFBAOT1 to -11 (hospital donors) and pFBAOT12 to -17 (fish farm donors). The cotransfer of other antibiotic resistances was assessed by screening E. coli J53-1 transconjugants for resistance to the antibiotics AP, minocycline, and TM in addition to those mentioned previously. Transconjugants containing plasmids pFBAOT6 (from the hospital) and pFBAOT13 (from the fish farm) were found, in addition to being OT resistant to be resistant to SM at 10 µg/ml but not at 25 µg/ml. The original isolates were also resistant to these antibiotics. Therefore, SM resistance was assumed to be plasmid encoded. Resistance to AP, minocycline, and TM was not observed in any of the transconjugants.Identification of host strains.
The identification of host
strains that carried the 17 transferable OTr plasmids is
shown in Table 2. Eight isolates were
identified as members of A. hydrophila DNA HG3 and contained
plasmids pFBAOT3 to -5, -7, -9 to -11 and -15. Six others were
identified as members of A. veronii bv. sobria HG8 (plasmids
pFBAOT1, -8, -12, -13, -14, and -17). The isolate that originally
carried pFBAOT16 could not be identified beyond the genus level (Table
2).
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Host range assessments. In an attempt to determine whether the pFBAOT plasmids are capable of transfer to recipients other than E. coli, conjugal transfer was carried out between each of the 17 original isolates and P. putida PaW340. Transfer of OTr to P. putida was demonstrated for plasmids pFBAOT3 to -7, -9, and -11. It was also shown that these plasmids could be retransferred from P. putida transconjugants back into OTs plasmid-free E. coli J53-1 (Table 2). These results suggested that pFBAOT3 to -7, -9, and -11 were potentially broad-host-range plasmids.
Molecular characterization of pFBAOT plasmids. We assessed which tet determinants and replicons were carried by the pFBAOT plasmids. Minipreparations of plasmids pFBAOT1 to -17 were screened by dot hybridization using the Tet A to E and Tet G probes and those specific to broad-host-range replicons N, P, Q, W, and U. It was shown that the Tet A determinant was carried by 10 plasmids (pFBAOT1, -3 to -7, -9, and -11 to -13) (Table 2), and no other characterized determinants were detected. Therefore, the remaining seven plasmids (pFBAOT2, -8, -10, -14, -15, -16, and -17) may possess previously undescribed tet determinants. Seven plasmids hybridized with the IncU probe (Table 2), and these were the same plasmids that displayed broad-host-range characteristics (plasmids pFBAOT3 to -7, -9, and -11). In addition, all of these plasmids carried Tet A (Table 2). The remaining 10 plasmids did not hybridize with the inc-rep probe set.
The dominance of determinant Tet A, as demonstrated in this study, is not uncommon (1, 24, 30), although the relatively small sample size of the present investigation may have precluded the detection of other determinants. The occurrence of Tet A alone in 19 Scottish A. salmonicida isolates recovered over a period of 11 years has been reported (1). In a study of 68 OTr plasmids from a diverse group of bacteria within the National Collection of Type Cultures, it was shown that Tet A and Tet B were carried most frequently (32.4 and 50% of the isolates, respectively), followed by Tet C (8.8%) and Tet D (5.9%), while 2.9% of the isolates that did not possess any of the determinants Tet A to E (24). Furthermore, Tet B was shown to be the most common determinant in bacteria isolated from pigs (30) while Tet E was dominant in marine sediments (3), as it was with Tet A and Tet D in A. hydrophila from cultured catfish (11, 12). Tet D has also been associated with other fish pathogens, including Pasteurella piscicida (now called Photobacterium damselae subsp. piscicida) and Edwardsiella tarda (5). Tet G has not been detected in any bacteria other than Vibrio anguillarum (35). It is therefore unsurprising that it was not detected in this study.Analysis of Tet A-containing plasmids.
The restriction
fragment length polymorphism (RFLP) patterns of plasmid DNA from Tet
A-carrying pFBAOT plasmids were compared after digestion with
EcoRI. Plasmids from hospital isolates were shown to be
closely related to each other, with pFBAOT7 and pFBAOT11 being
identical (Fig. 1A). Plasmid extractions
from fish farm E. coli transconjugants were repeatedly of
poor quality, and so RFLP patterns for plasmids pFBAOT12 to -17 were
difficult to interpret. For this reason, the profiles of these plasmids
are absent from Fig. 1. However, it was clear that they did not share
close homology and were larger than the hospital-derived plasmids
(pFBAOT1 to -11) (data not shown). Two EcoRI restriction
fragments of approximately 5.2 and 5.5 kb were common to seven of the
eight Tet A-carrying hospital-derived plasmids (pFBAOT3 to -7, -9, and
-11). pFBAOT1, which was not IncU (and therefore was not included in
Fig. 1) and was originally found in A. veronii bv. sobria
HG8, carried only the 5.5-kb fragment. In addition, common fragments of
approximately 5.7 and 6.5 kb were observed in pFBAOT3 to -5, -7, -9, and -11 (all originally found in A. hydrophila HG3) but were
absent from pFBAOT1 and -6 (from A. caviae HG5A) (Fig. 1A;
see Fig. 4A). It was difficult to discern from RFLP data alone whether
any of the fish farm-derived plasmids carried these common fragments.
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Cloning and partial sequencing of the 5.5-kb EcoRI Tet
A-carrying fragment.
The results presented here show that the
5.5-kb EcoRI Tet A-carrying fragment is more widespread than
has been previously suggested (1) and that it is not
exclusively associated with IncU plasmids. This fragment was shotgun
cloned from plasmid pFBAOT6 into pUC18, and sequencing was carried out
from each end of the cloned insert such that partial sequences of 647 and 620 bp were obtained. The first 647 bp of one end of the insert
shared 95% homology with Tn1721 (encompassing the first
right inverted repeat (IRR-I), the tccA gene
(27), and part of the tetR gene, respectively). The first 620 bp of the opposite end of the insert shared 95% homology
with IRR-II and part of the tnpA' region of
Tn1721 (data not shown). This demonstrated that the 5.5-kb
EcoRI fragment from pFBAOT6 was highly homologous to
the 5.5-kb EcoRI fragment found in Tn1721. In
order to assess whether the complete transposon Tn1721 was
present on these plasmids, a DNA probe was constructed from
plasmid pMT1286 (45) that was specific to the gene
(orfI) which encodes MCP, situated at the left-hand end of
Tn1721 (2) (Fig.
3). This probe was hybridized to plasmid
pASOT (pASOT2 and pASOT3 were not assessed), pIE420, and the IncU
pFBAOT plasmids. The results showed that all of the IncU
pFBAOT plasmids and pASOT carry this gene, unlike plasmid
pIE420 (Fig. 4C). Plasmids pFBAOT3, -4, -5, -7, -9, and -11 carry the MCP-encoding gene on a 5.6- to 5.8-kb
EcoRI fragment (slightly larger than the region
carrying the Tet A determinant). Plasmid pFBAOT5 also carried a
second copy of the gene on a fragment of approximately 12 to 13 kb,
suggesting that this plasmid contains two copies of a
Tn1721-like element. Plasmid pASOT carries the region on a
7-kb EcoRI restriction fragment, while a 9-kb fragment was
detected in pFBAOT6 (Fig. 4). The presence of the MCP region on a 5.6- to 5.8-kb EcoRI fragment, in addition to a 5.5-kb Tet
A-carrying EcoRI fragment, is indicative of possession of
the complete Tn1721 transposon (Fig. 3). Therefore, plasmids pFBAOT3 to -5, -7, -9, and -11 appear to possess complete transposon sequences (indicating that the MCP-encoding gene-containing region is
5,610 bp in length; Fig. 3). The differences between this group and pASOT and pFBAOT6 might be explained in light of recent
findings by Schnabel and Jones (39). They demonstrated that
the Tet A-mediated TC resistance observed in phylloplane
Pseudomonas sp. was due to a truncated form of
Tn1721 (designated Tn1720).
Tn1720 lacks the MCP-encoding region (orfI)
and has minor variations in the sequence of the three inverted repeats
on Tn1721. This variation within the left inverted repeat
(IRL) resulted in an alteration at the EcoRI site
(39). Plasmids pASOT and pFBAOT6 possessed the MCP-encoding
region and therefore did not harbor Tn1720. However, the
location of the MCP-encoding region on fragments larger than 5.6 kb
along with a 5.5-kb Tet A-carrying EcoRI fragment is
indicative of the loss of the EcoRI site within the IRL. The
absence of the MCP-encoding region from pIE420 suggested that it may
contain a Tn1720-like transposon. If this were the case,
then the transposition genes tnpR and tnpA would
still be present on the plasmid. To test this hypothesis, the plasmid
was probed with the complete Tn1722 transposon and no
hybridization signal was obtained (data not shown). This result
suggested that the 5.5-kb Tet A-carrying EcoRI fragment was
deposited by Tn1721 but with subsequent loss of
minitransposon Tn1722 (Fig. 3). This scenario might also be applicable to the unrelated plasmids pFBAOT1, -12, and -13, which also
carry Tet A on the 5.5-kb EcoRI fragment.
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Conclusions. Adams et al. (1) highlighted the need for research on OT usage in aquaculture and the resistance associated with relevant bacteria to extend to isolates from other geographical locations and to other fish pathogens. In addition, these authors highlighted the need to determine whether these resistance plasmids extend beyond fish farm environments (1). The main objectives of this study were to carry out these assessments and to investigate whether the aquaculture and human compartments of the environment should be considered separate entities with distinct transfer events or a single interactive compartment of the environment. In the course of these analyses, we showed that closely related IncU R plasmids previously associated only with fish farm environments were common to those impacting humans (i.e., pASOT plasmids and pRAS1 from fish farms and pFBAOT plasmids and pIE420 from hospital sewage and a German hospital patient, respectively). In addition, this dissemination occurred among at least four separate countries (Norway, Scotland, England, and Germany). Furthermore, the occurrence of pFBAOT plasmids in A. hydrophila and A. caviae demonstrated that they could disseminate to other related bacteria under natural conditions. This study also showed for the first time that plasmids pRAS1 and pIE420 are probably identical. The original carriage of pIE420 in E. coli (44) and pRAS1 in A. salmonicida (37) demonstrated interspecies transfer from (or to) a human commensal (and potentially pathogenic) organism under natural conditions. Collectively, these findings provide evidence that suggests that we should consider the two environments (fish farm and hospital) one interactive compartment and are therefore contrary to the hypothesis of Smith and coworkers (40). The involvement of Tn1721 and Tn1721-like elements in the dissemination of the Tet A determinant, as demonstrated here and by other workers (13, 39), is extremely relevant to this interaction and, globally, to the potential dissemination of these and similar plasmids.
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ACKNOWLEDGMENTS |
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The support of the European Community (FAIR CT96 1703) is gratefully acknowledged.
We thank Louisa Faulkner for technical assistance and Ruth-Anne Sandaa, Dougie McIntosh, Joyce Petri, Erhard Tietze, and Masataka Tsuda for provision of plasmid-containing control strains.
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FOOTNOTES |
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* Corresponding author. Mailing address: Freshwater Biological Association, The Ferry House, Far Sawrey, Ambleside, Cumbria LA22 OLP, United Kingdom. Phone: 44 (015394 42468). Fax: 44 (015394 46914). E-mail: glenn{at}ceh.ac.uk.
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