Effects of residual antibiotics in groundwater on Salmonella typhimurium: changes in antibiotic resistance, in vivo and in vitro pathogenicity†
Received
2nd September 2011
, Accepted 24th October 2011
First published on 4th November 2011
Abstract
An outbreak-causing strain of Salmonella enterica serovar Typhimurium was exposed to groundwater with residual antibiotics for up to four weeks. Representative concentrations (0.05, 1, and 100 μg L−1) of amoxicillin, tetracycline, and a mixture of several other antibiotics (1 μg L−1 each) were spiked into artificially prepared groundwater (AGW). Antibiotic susceptibility analysis and the virulence response of stressed Salmonella were determined on a weekly basis by using human epithelial cells (HEp2) and soil nematodes (C. elegans). Results have shown that Salmonella typhimurium remains viable for long periods of exposure to antibiotic-supplemented groundwater; however, they failed to cultivate as an indication of a viable but nonculturable state. Prolonged antibiotics exposure did not induce any changes in the antibiotic susceptibility profile of the S. typhimurium strain used in this study. S. typhimurium exposed to 0.05 and 1 μg L−1amoxicillin, and 1 μg L−1tetracycline showed hyper-virulent profiles in both in vitro and in vivo virulence assays with the HEp2 cells and C. elegans respectively, most evident following 2nd and 3rd weeks of exposure.
Environmental impact
Salmonella enterica serovar Typhimurium is one of the most problematic enteric pathogens, with a high percentage of multiple antibiotic-resistant strains. As a resilient pathogen, it can cope well with a variety of stress conditions both in host and natural environments. Therefore, it is critical to understand how the stress conditions affect the viability and pathogenicity of S. typhimurium. This investigation found with the groundwater and antibiotic exposure, S. typhimurium can remain viable for long periods of exposure. Antibiotic susceptibility analysis and the virulence response of Salmonella were determined using human epithelial cells and soil nematodes. One notable observation was S. typhimurium exposed to residual amoxicillin and tetracycline showed hyper-virulent profiles in our virulence assays.
|
Introduction
Salmonella enterica serovar Typhimurium is one of the most problematic food- and waterborne enteric pathogens in the world, with a high percentage of multiple antibiotic-resistant strains frequently isolated.1 As a resilient pathogen, Salmonella typhimurium can cope well with a variety of stress conditions including temperature, osmolarity, and pH, both in its target host and in natural environments.2,3 One of the most common matrices that Salmonella contaminates is groundwater systems,4–8 frequently used as source water for direct consumption or vegetation watering practices. As a result, numerous cases of food and waterborne related Salmonella outbreaks are on the rise as indicated by recent reports from CDC.9 Therefore, it is critically important to understand how the stress conditions imposed in groundwater environments affect the viability and pathogenicity of S. typhimurium.10
Pharmaceutical products are also major contaminants of aquatic systems11–15 and the majority of the pharmaceutical products found in both surface and groundwater systems are antibiotics.16–19 Although the resistance mechanisms of S. typhimurium against antibiotics are a widely explored topic,20–24 there still exists a knowledge gap in overall bacterial response to antibiotics as an environmental stress condition and how exposure to low levels of antibiotic affect viability and pathogenicity.
The goal of this study was to understand the effects of stress induced by groundwater environments and antibiotic presence on the viability, pathogenicity, and antibiotic susceptibility of S. typhimurium for prolonged exposure periods. To fulfil this goal, artificial groundwater was prepared and the conditions were simulated with residual antibiotics. Due to persistence25–28 and prevalence in the environment,11,13–15amoxicillin and tetracycline were selected as the candidate antibiotics. To represent a wide range of pristine and contaminated groundwater conditions, both low15,29 and high30 concentrations of antibiotics were used.13,14 In addition to amoxicillin and tetracycline, a cocktail of antibiotics was prepared by mixing nine common antibiotics and spiked into the groundwater. Antibiotic susceptibility analysis of stressed cells, along with in vitro and in vivo virulence assays, were performed for S. typhimurium exposed to these combinations of antibiotics for up to four weeks. Results indicated that long-term exposure to groundwater supplemented with residual antibiotics may increase the virulence of S. typhimurium against human epithelial cells and nematodes. During the course of the study, bacteria remained mostly viable; however, they failed to cultivate. No further antibiotic resistance was gained in any of the tested isolates due to exposure to the tested antibiotics.
Materials and methods
Bacterial cell growth and preparation
Salmonella enterica serovar Typhimurium strain ST5383 used in this study was obtained from the Salmonella Genetic Stock Centre (SGSC) of University of Calgary, Alberta, Canada. S. typhimurium strain ST5383 is a wild-type strain originally isolated from an interprovincial outbreak that infected more than 1700 people.31Salmonellacells used during the course of study were cultured in Luria-Bertani (LB) broth, (Fisher Scientific, Fair Lawn, NJ) at 37 °C overnight, shaken continuously at 120 rpm. A refrigerated bench-top centrifuge (5804R; Eppendorf, Hamburg, Germany) equipped with fixed angle rotor (F-34-6-38; Eppendorf) was used to pellet the cells with an applied 3700 × g force for 15 min at 4 °C. Growth medium was decanted and the pellet was resuspended in 3 mM in prepared groundwater. The concentration of cell stock solution was determined by using a cell counting hemocytometer (Bürker-Turk, Germany) under a light microscope (Fisher Scientific).
Application of stress conditions
Bacteria cultured and harvested as described above were exposed to several antibiotics containing groundwater for 1 to 4 weeks. Groundwater solutions used in cell preparation and other experiments were prepared with de-ionized water (DIW) (Millipore, Billerica, MA) and reagent-grade salts (Fisher Scientific) with a slight modification to a previously used artificial groundwater recipe32 by dissolving following in one liter of DIW: CaCl2·2H2O (36mg), CaSO4·2H2O (25mg), KNO3 (20mg), NaHCO3 (36mg), Ca(NO3)2·4H2O (35mg), and MgSO4·7H2O (60mg). The pH of solutions was kept constant at 7.0 ± 0.2. The ionic strength (IS) of the solutions tested was 3 mM, typical for groundwater.33,34
The levels of antibiotics added to groundwater were 0.05, 1, and 100 μg L−1ampicillin (MP Biomedicals, Solon, OH); 0.05, 1, and 100 μg L−1tetracycline (MP Biomedicals), and a cocktail of 1 μg L−1 of each the following antibiotics: amoxicillin, streptomycin, gentamicin, sulfamethoxazole (MP Biomedicals), tetracycline, ampicillin, chloramphenicol, kanamycin (EMD Chemicals, Darmstadt, Germany), and penicillin (Fisher Scientific).
A bacterial suspension containing 107cells mL−1 was exposed to the aforementioned stress conditions in 500-mL tissue culture flasks with phenolic caps (Corning, MA) to minimize gas-exchange, and wrapped with aluminum foil to minimize light exposure. The flasks were placed on orbital shakers, and mildly shaken (70 rpm) at room temperature for the desired time periods.
Viability and cultivability
At the end of exposure to groundwater with residual antibiotics, viability of the cells was determined by using the Live/Dead BacLight® kit (L-7012; Molecular Probes, Eugene, OR) according to the manufacturer's directions. Direct counting of the stained live and dead cells was done using an inverted microscope (IX70; Olympus, Japan) operated under a red/green fluorescence filter set (Chroma Technology Corp., Brattleboro, VT). Stressed organisms were also tested for loss of cultivability by spread plating serial dilutions of stressed cells on LB agar (Fisher Scientific) plates followed by overnight incubation at 37 °C. Colony forming units (CFUs) were enumerated the following day.
Antibiotic susceptibility analysis
Antibiotic susceptibility tests were employed to assess the changes in S. typhimurium's resistance to 11 antimicrobial substances commonly used by the U.S. National Antimicrobial Resistance Monitoring System (NARMS). Tests were performed in compliance with the Clinical and Laboratory Standards Institute/National Committee for Clinical Laboratory Standards (CLSI/NCCLS)35 for the following antimicrobial agents (numbers in parentheses denote the amount of antimicrobial substance impregnated in 6 mm disks): amikacin (30 μg), amoxicillin-clavulanic acid (30 μg), cefoxitin (30 μg), ceftriaxone (30 μg), ceftiofur (30 μg), cephalothin (30 μg), chloramphenicol (30 μg), ciprofloxacin (5 μg), nalidixic acid (30 μg), tetracycline (30 μg), trimethoprim-sulfamethoxazole (25 μg). Antibiotic susceptibility analyses were performed in triplicate.
In vitro invasion assays
Human epithelial cell line HEp2 was obtained from American Type Culture Collection (CCL-23; ATCC, Manassas, VA) and cultured in Eagle's Minimum Essential Medium (ATCC) supplemented with 10% fetal bovine serum (ATCC), and 1% penicillin-streptomycin (Sigma-Aldrich, St. Louis, MO). Epithelial cells were incubated at 37 °C under 5% CO2 atmosphere.
Invasion of stressed S. typhimurium into epithelial cells was quantified with slight modifications to a protocol as described elsewhere.36 Briefly, a monolayer of HEp2 cells was grown until confluence in 24-well plates (Corning, Corning, NY), and was subsequently inoculated with 105Salmonellacells and incubated for 2 h at 37 °C to allow for internalization. Following the incubation, each well was washed three times with phosphate buffered saline (PBS) to remove unbound bacteria. Bacteria that were bound to the epithelial cells, but had not been internalized, were killed by applying fresh growth medium containing penicillin and gentamicin (5 and 100 μg mL−1 respectively); the plates were then incubated for 2 h at 37 °C. Following incubation, cells were washed with PBS, treated with trypsin-EDTA complex (ATCC), and lysed with 1% Triton-X100 (Fisher). The lysates were spread onto LB agar plates and incubated for 18 h at 37 °C. The CFUs were counted to quantify the number of S. typhimurium that had successfully invaded the monolayer of epithelial cells. Invasion assays and CFU enumeration were performed in triplicate.
Caenorhabditis elegans maintenance and in vivo virulence assays
C. elegans strain SS104 [glp-4 (ts)], a temperature-sensitive mutant of nematode worms that produces progeny at 15 °C but not at 25 °C,37 was obtained from the Caenorhabditis Genetics Center (University of Minnesota, Saint Paul) and used for virulence assays. Worms were maintained by slight modifications to standard procedures described elsewhere.38 Briefly, worms were grown on modified nematode growth medium (NGM) (US Biological, Swampscott, MA) [with 0.35% peptone instead of 0.25%, and supplemented with uracil (Fisher Scientific) (2 g L−1 final concentration)] plates at 15 °C, and fed with nonpathogenic E. coli strain OP50 as previously described.39
Virulence assays were performed based on similar studies described in literature.40–42 Fifteen synchronized worms in larval stage L4 were transferred to fresh NGM plates seeded with 10 μL of stressed S. typhimuriumcells (from the antibiotics containing groundwater flasks) mixed with E. coliOP50 (1
:
100 ratio respectively), and maintained at 25 °C. The number of viable worms was counted daily and reported as the number of survivors until all fifteen worms were killed. Worms that were sessile and unresponsive to touch were considered to be dead. For each stress condition, virulence assays were performed in triplicate. The control group was only fed with E. coliOP50.
Statistical analysis of data
Changes in the diameters of antibiotic inhibition zones and the number of CFUs of S. typhimurium infecting HEp2 cells were statistically compared to the control groups using unpaired Student's t-test using Minitab® Version 14 (State College, PA). Differences between control and stressed Salmonellacells were considered to be significant at 95% confidence interval (P < 0.05).
Results
Viability and cultivability of Salmonella typhimurium
Changes in the percent viability and cultivability of S. typhimurium exposed to antibiotic-containing groundwater were determined with respect to time and reported in Fig. 1 and 2, respectively. As can be seen from Fig. 1, the percent viability of the control group that was not exposed to antibiotics, i.e., week 0, ranged from 92% to 100%. As anticipated, the percentage of viable cells decreased gradually as cells were exposed to antibiotic-containing groundwater for longer time periods (2 and 3 weeks) (Fig. 1). By the end of week 4, the percent viabilities of cells exposed to amoxicillin were 38%, 41%, and 34% for concentrations of 0.05, 1, and 100 μg L−1, respectively. The percent viabilities of the cells exposed to tetracycline were 37% and 32% for concentrations of 0.05 and 1 μg L−1, respectively. At higher tetracycline concentrations, i.e., 100 μg L−1, the percent viability was much lower (14%). The lowest percent viability (12%) was observed in batch exposed to the cocktail of antibiotics at the end of week 4.
 |
| Fig. 1 Changes in percent viability of S. typhimurium exposed to antibiotics-containing AGW with respect to time and compared to control group. The abbreviations in the legend refer to the tested antibiotics (AMO for amoxicillin, and TE for tetracycline). The numbers in the legend refer to the concentrations of tested antibiotics in μg L−1. Error bars indicate the standard deviation of three replicates. | |
 |
| Fig. 2 Changes in percent cultivability of S. typhimurium exposed to antibiotics-containing AGW with respect to time and compared to control group. The abbreviations in the legend refer to the tested antibiotics (AMO for amoxicillin, and TE for tetracycline). The numbers in the legend refer to the concentrations of tested antibiotics in μg L−1. Error bars indicate the standard deviation of three replicates. | |
During the course of study, the loss of cultivation in S. typhimuriumcells was also monitored and reported as percent cultivability (Fig. 2). The initial (week 0) cultivability percentages were very close to the percentages of determined viability; however, significant differences were observed between percent viability and cultivability values starting at the end of week 1 and persisting through the end of week 4. The cells exposed to a low concentration of amoxicillin were 85% and 74% cultivable (for 0.05 and 1 μg L−1 respectively); however, only 13% cultivability was observed for cells exposed to the 100 μg L−1 of amoxicillin. In the case of tetracycline-exposed cells, the cultivability was 52% and 70% for 0.05 and 1 μg L−1, respectively. In the case of high concentration of tetracycline exposure (100 μg L−1), none of the cells were capable of being cultivated by the end of week 1. This was also observed for the cells exposed to the cocktail of antibiotics (Fig. 2). Similar to the trend observed in percent viability measurements, the cultivability of cells in the presence of amoxicillin decreased during the exposure period of week 2 and week 3. The cells exposed to the high concentration of tetracycline and the cocktail of antibiotics failed to cultivate following weeks 2, 3 and 4. By the end of week 4, percent cultivability was relatively low for the rest of the conditions: 14% and 11% (for 0.05 and 1 μg L−1amoxicillin exposure, respectively), 1% (for 1 μg L−1amoxicillin exposure), as well as 6% and 2% (for 0.05 and 1 μg L−1tetracyclin exposure, respectively). No growth was observed after 4 weeks of exposure to either 100 μg L−1tetracycline or the cocktail of antibiotics (Fig. 2).
Antibiotic susceptibility analysis
The full names and abbreviations of all antibiotics used for the susceptibility tests are presented in SI Table S1, along with the resistance breakpoints indicating the thresholds of susceptible, intermediate resistance, and resistant levels.35 As further indication and confirmation of low levels or no cultivability in bacteria exposed to high concentrations of antibiotics (exposure to 100 μg L−1 of amoxicillin and tetracycline, and the cocktail of antibiotics), no bacteria were observed on the antibiotic susceptibility plates and therefore these tests were not performed.
Table S2 shows the measured diameters of the zones of inhibition for S. typhimurium exposed to groundwater with residual amoxicillin (0.05 μg L−1). Week 0 data denote the susceptibility profile of the control group consisting of the cells that were not exposed to antibiotic stress. As can be seen in Table S2, the control group of S. typhimurium strain used in this study (ST5383) was susceptible to all 11 antibiotics tested. As cells were exposed to a low concentration of amoxicillin (0.05 μg L−1), subtle increases were observed in the size of the inhibition zone. These increases were statistically significant for only a few cases as indicated in Table S2. Similarly, exposure to groundwater with 1 μg L−1amoxicillin did not change the susceptibility profile of the control group for any of the antibiotics tested. As can be seen in Table S3, the zone diameters increased for the majority of the cells during the exposure period from week 1 to week 4.
Antibiotic susceptibility of cells exposed to tetracycline-containing groundwater resulted in similar trends to the amoxicillin exposure. The inhibition zone diameters are given in Table S4 and Table S5 for tetracycline concentrations of 0.05 and 1 μg L−1, respectively. The results indicate that cells exposed to tetracycline-containing groundwater sustained their susceptibility to the tested antibiotics for the duration of week 1 to week 4 for either concentration of tetracycline.
In vitro invasion assays
The number of S. typhimuriumcells (denoted as CFUs) that can successfully invade human epithelial cell cultures (HEp2) following the exposure to antibiotic-containing groundwater were presented in Table 1. Prior to the groundwater exposure (week 0) 258 CFUs from the control group invaded HEp2 cells. At the end of week 1, the CFUs decreased significantly to 192 for cells exposed to tetracycline (0.05 μg L−1), and 128 and 64 for cells exposed to amoxicillin (0.05 and 100 μg L−1, respectively) (P < 0.05). However, cells exposed to amoxicillin and tetracycline (both 1 μg L−1) resulted in the number of CFUs that could invade HEp2 cells to increase significantly to 448 and 384, respectively (P < 0.05). None of the cells exposed to the cocktail of antibiotics and high concentration of tetracycline (100 μg L−1) were able to invade HEp2 cells for the remaining duration of the study. By the end of week 2, the number of CFUs has dramatically increased to 2667 and 1600 for cells exposed to 0.05 and 1 μg L−1amoxicillin, respectively. The number of CFUs that can invade HEp2 cells was 107 for 100 μg L−1amoxicillin-exposed cells, which is higher than week 1 results but still less than the control group. Among the cells exposed to 1 μg L−1tetracycline, none of them were able to invade the epithelial cells starting from week 1 to the end of the study. At the end of week 3, the number of CFUs from amoxicillin-exposed cells (0.05 and 1 μg L−1) was significantly higher than the control group; however, it was less than week 2 exposed cells. By the end of the study, the number of CFUs that could successfully invade the epithelial cells was less than those of the control group, except for cells exposed to the high concentration of amoxicillin (100 μg L−1).
Table 1 Number of S. typhimurium CFUs infecting HEp2 cells exposed to antibiotics containing groundwater with respect to time and compared to control group
Stress conditions |
Week 0 |
Week 1 |
Week 2 |
Week 3 |
Week 4 |
Numbers in bold denote the changes in the CFUs are statistically significant compared to the control group.
|
Amoxicillin (0.05 μg L−1) |
|
128 ± 18a |
2667 ± 269 |
720 ± 83 |
213 ± 45 |
Amoxicillin (1 μg L−1) |
|
448 ± 56 |
1600 ± 127 |
480 ± 57 |
107 ± 39 |
Amoxicillin (100 μg L−1) |
|
64 ± 12 |
107 ± 18 |
400 ± 38 |
320 ± 49 |
Tetracycline (0.05 μg L−1) |
258 ± 34 |
192 ± 24 |
0 |
0 |
0 |
Tetracycline (1 μg L−1) |
|
384 ± 28 |
320 ± 34 |
320 ± 42 |
53 ± 17 |
Tetracycline (100 μg L−1) |
|
0 |
0 |
0 |
0 |
Cocktail (1 μg L−1) |
|
0 |
0 |
0 |
0 |
In vivo virulence assays
To confirm the virulence trends of stressed S. typhimuriumcells against HEp2 cells, in vivo virulence assays were performed with C. elegans and the results are presented in Fig. 3. Worms that were fed with E. coliOP50 and S. typhimuriumcells not exposed to stress conditions were referred as the control group. As can be seen in Fig. 3, the control group died in 17 days. When E. coliOP50 was mixed with S. typhimuriumcells exposed to amoxicillin (for concentrations of 0.05, 1 and 100 μg L−1) and tetracycline (1 μg L−1) for the durations of one to four weeks, worms died in a shorter period of time than the control group. S. typhimurium exposed to tetracycline (for concentrations of 0.05 and 100 μg L−1) and the cocktail of antibiotics killed the worms in 16 and 17 days, respectively, which is very similar to the control group (data not shown). S. typhimuriumcells exposed to 1 μg L−1tetracycline for one week were able to kill worms in 13 days (Fig. 3). The cells exposed to tetracycline (1 μg L−1) for two weeks or later resulted in very similar results to the control group as well (data not shown; P > 0.05).
 |
| Fig. 3 Number of C. elegans remaining alive when fed with S. typhimurium exposed antibiotic-containing groundwater for one week (a), two weeks (b), three weeks (c), and four weeks (d). The abbreviations in the legend refer to the tested antibiotics (AMO for amoxicillin, and TE for tetracycline). The numbers in the legend refer to the concentrations of tested antibiotics in μg L−1. All experiments were performed in triplicates, error bars are not shown for clarity purposes. | |
S. typhimurium
cells exposed to low concentrations of amoxicillin-containing groundwater were the fastest killers of the worms as an indication of hyper-virulence.43–45 It took 10, 7, 9, and 11 days to kill all the worms after one, two, three, and four weeks of exposure to 0.05 μg L−1amoxicillin, respectively. For 1 μg L−1amoxicillin-exposed cells, worms were dead in 11, 8, 10, and 12 days (week 1, 2, 3, and 4 exposure, respectively). Exposure to a high concentration of amoxicillin (100 μg L−1) and tetracycline (1 μg L−1) showed similar results in terms of the days required to kill all worms.
Discussion
It is widely accepted that human pathogenic bacteria enter the viable but nonculturable (VBNC) state when exposed to harsh environmental conditions.46–48 However, it is a matter of continuous debate whether or not VBNC cells pose a risk to human and animal health.48–52 Therefore, both percent viability and cultivability values were determined (Fig. 1 and 2, respectively). Results have shown that although the cells remain viable, they may not be cultivable at all (e.g., exposure to 100 μg L−1tetracycline and cocktail of antibiotics from week 1 to week 4) or cultivable at low levels [e.g., exposure to 100 μg L−1amoxicillin from week 1 to week 4 and lower concentrations of tetracycline (0.05 and 1 μg L−1) from week 2 to week 4]. Overall, the results showed that the majority of the cells exposed to antibiotics for up to two weeks may remain structurally intact53 (as determined by viability); however, they fail to cultivate. As the exposure time to antibiotics is prolonged, both the percent viability and cultivability decreases to minimal levels (Fig. 1 and 2, respectively).
The antibiotic susceptibility tests could not be performed for the cells that failed to cultivate [tetracycline (100 μg L−1), and cocktail of antibiotics]. This was also the case for cells exposed to groundwater with the high concentration of amoxicillin (100 μg L−1), due to the low cultivability (Fig. 2). Antibiotic susceptibility tests were successfully performed for cells exposed to groundwater with tetracycline (0.05 and 1 μg L−1), even though they showed similar cultivability (especially after week 2) to cells exposed to groundwater with high concentration of amoxicillin (100 μg L−1). This may be due to the fact that different media were used for the cultivability (LB agar) and antibiotic susceptibility (Mueller-Hinton agar) tests, resulting in different growth characteristics.
Results of the antibiotic susceptibility tests were quite unexpected (Tables S2–S5). As bacteria are exposed to antibiotics in different aquatic, terrestrial, and host habitats, it is inevitable that resistance is gained to those antibiotics.11,24,54–57 However, there was no increased amoxicillin resistance induced by exposure to this antibiotic condition during the prolonged duration of this study. On the contrary, the cells showed increased susceptibility (Tables S2, S3). This observation was also confirmed with tetracycline exposure: the susceptibility of cells exposed to 0.05 and 1 μg L−1 of tetracycline-containing groundwater showed increased susceptibility to tetracycline (Tables S4, S5). This may be explained by the following mechanisms. First, the concentration of the antibiotics tested might be too low (0.05 and 1 μg L−1) to induce resistance in the bacteria. This hypothesis could have been confirmed with the cells exposed to high concentrations of antibiotics; however, the tests failed as mentioned earlier. Secondly, although both tetracycline25–27 and amoxicillin28 are quite resistant to degradation, they might have been degraded in the groundwater with time11,16,58 and resulted in a lesser or insignificant level of activity.59
Usage of human epithelial cell lines to test the in vitro virulence of Salmonella is a quite common and effective way of analyzing the degree of pathogenicity.60–63 However, in vitro virulence assays may not fully represent the internal habitat of a living organism. Therefore, the commonly-studied soil nematode C. elegans64 was utilized to test the in vivo virulence of S. typhimurium40–42,65–68 exposed to antibiotic-containing groundwater as a complement to in vitro assays. In vitro virulence assays have shown that exposing S. typhimurium to antibiotic-containing groundwater may increase the virulence of the bacteria as indicated by a greater number of cells entering the host epithelial cell lines (Table 1). This was more evident for cells exposed to a low concentration of amoxicillin during weeks 2 and 3. The changes in CFUs involved in invasion were not pronounced for week 1 and week 4 under the low concentration amoxicillin condition. The cells exposed to high (100 μg L−1) and low (0.05 and 1 μg L−1) (after week 1) concentrations of tetracycline and the cocktail of antibiotics did not invoke virulence against HEp2 cells as described earlier.
In vivo virulence assays were in agreement with the in vivo virulence assays: the worms were killed in a shorter amount of time with S. typhimurium exposed to a low concentration of amoxicillin for two and three weeks as compared to the control group (Fig. 3b, c). Cells exposed to stress conditions for four weeks were still virulent to C. elegans; however, the days required to kill the whole population was longer than those exposed for one to three weeks (Fig. 3).
The reason for increased virulence at exposure periods of two and three weeks may be that the cells were becoming accustomed to the exposed stress conditions during the first week and eventually adjusted their metabolism to the groundwater environment during the following weeks. This has been proven with K+, Ca2+ and Mg2+ ions (all present in groundwater), known promoters of increased virulence of S. typhimurium.69–74 The decreased virulence observed in week 4 is possibly due to cells starting to die and lose their infectious characteristics as indicated by viability and cultivability data (Fig. 1, 2). This is in agreement with another study that has shown that S. typhimurium stressed with UV-C light and seawater may lose its cultivability and virulence, whereas it remained structurally intact and viable.75
Conclusions
In this study, evidence that long-term exposure (up to approximately one month) to groundwater supplemented with several antibiotics may induce a viable but nonculturable (VBNC) state in Salmonella typhimurium was obtained. It has been also shown that S. typhimurium remains viable in groundwater up to four weeks. During the course of the study, S. typhimurium exposed to low-concentration amoxicillin-containing groundwater for two and three weeks showed hyper-virulence against human epithelial (HEp2) cells and nematodes (C. elegans) as shown by both in vitro and in vivo virulence assays, respectively. Enhanced virulence was also observed to be due to exposure to groundwater with a representative concentration of tetracycline. Exposure of S. typhimurium to amoxicillin- and tetracycline-containing groundwater up to four weeks did not induce any resistance against these antibiotics among the bacteria. These results suggest that S. typhimurium in groundwater contaminated with trace antibiotics may remain viable and may show increased virulence to either human and/or animal hosts.
Acknowledgements
The authors acknowledge funding from the U.S. Department of Agriculture CSREES HSI (#2006-38422-17086) and NRI (#2007-35102-18262) programs. We thank Gina Broitman-Maduro for her assistance with the C. elegans.
References
-
CDC, Salmonella Surveillance: Annual Summary, 2006, US Department of Health and Human Services, Atlanta, GA, 2006 Search PubMed.
- J. W. Foster and M. P. Spector, Annu. Rev. Microbiol., 1995, 49, 145–174 CrossRef CAS.
- M. A. S. McMahon, J. Xu, J. E. Moore, I. S. Blair and D. A. McDowell, Appl. Environ. Microbiol., 2006, 73, 211–217 CrossRef.
- R. Taylor, D. Sloan, T. Cooper, B. Morton and I. Hunter, Commun. Dis. Intell., 2000, 24, 336–340 CAS.
- F. J. Angulo, S. Tippen, D. J. Sharp, B. J. Payne, C. Collier, J. E. Hill, T. J. Barrett, R. M. Clark, E. E. Geldreich, H. D. Donnell, Jr and D. L. Swerdlow, Am. J. Public Health, 1997, 87, 580–584 CrossRef CAS.
- B. J. Haley, D. J. Cole and E. K. Lipp, Appl. Environ. Microbiol., 2009, 75, 1248–1255 CrossRef CAS.
- I. G. Droppo, S. N. Liss, D. Williams, T. Nelson, C. Jaskot and B. Trapp, Environ. Sci. Technol., 2009, 43, 1737–1743 CrossRef CAS.
- W. Ahmed, S. Sawant, F. Huygens, A. Goonetilleke and T. Gardner, Water Res., 2009, 43, 4918–4928 CrossRef CAS.
-
CDC, Outbreaks Involving Salmonella, http://www.cdc.gov/salmonella/outbreaks.html, accessed August 14, 2011 Search PubMed.
- W.-T. Liu, M. H. Karavolos, D. M. Bulmer, A. Allaoui, R. D. C. E. Hormaeche, J. J. Lee and C. M. Anjam Khan, Microb. Pathog., 2007, 42, 2–10 CrossRef CAS.
- A. K. Sarmah, M. T. Meyer and A. B. A. Boxall, Chemosphere, 2006, 65, 725–759 CrossRef CAS.
- D. G. Capone, D. P. Weston, V. Miller and C. Shoemaker, Aquaculture, 1996, 145, 55–75 CrossRef CAS.
- K. Kümmerer, Chemosphere, 2009, 75, 435–441 CrossRef.
- K. Kümmerer, Chemosphere, 2009, 75, 417–434 CrossRef.
- O. A. H. Jones, N. Voulvoulis and J. N. Lester, Water Res., 2002, 36, 5013–5022 CrossRef CAS.
- R. Hirsch, T. Ternes, K. Haberer and K.-L. Kratz, Sci. Total Environ., 1999, 225, 109–118 CrossRef CAS.
- K. G. Karthikeyan and M. T. Meyer, Sci. Total Environ., 2006, 361, 196–207 CrossRef CAS.
- T. Heberer, Toxicol. Lett., 2002, 131, 5–17 CrossRef CAS.
- F. Sacher, F. T. Lange, H. J. Brauch and I. Blankenhorn, J. Chromatogr., A, 2001, 938, 199–210 CrossRef CAS.
- J. Zheng, S. Cui and J. Meng, J. Antimicrob. Chemother., 2008, 63, 95–102 CrossRef.
- K. Nishino, M. Hayashi-Nishino and A. Yamaguchi, Antimicrob. Agents Chemother., 2009, 53, 3541–3543 CrossRef CAS.
- S. Feuerriegel and P. Heisig, Microb. Drug Resist., 2008, 14, 259–263 CrossRef CAS.
- K. Nishino and A. Yamaguchi, Biosci. Microflora, 2008, 27, 75–85 CAS.
- S. D. Alcaine, L. D. Warnick and M. Wiedmann, J. Food Prot., 2007, 70, 780–790 CAS.
- G. Hamscher, S. Sczesny, H. Hoper and H. Nau, Anal. Chem., 2002, 74, 1509–1518 CrossRef CAS.
- A. Pruden, R. Pei, H. Storteboom and K. H. Carlson, Environ. Sci. Technol., 2006, 40, 7445–7450 CrossRef CAS.
- D. S. Aga, S. O'Connor, S. Ensley, J. O. Payero, D. Snow and D. Tarkalson, J. Agric. Food Chem., 2005, 53, 7165–7171 CrossRef CAS.
- X. Pan, C. Deng, D. Zhang, J. Wang, G. Mu and Y. Chen, Aquat. Toxicol., 2008, 89, 207–213 CrossRef CAS.
- S. Yang and K. Carlson, Water Res., 2003, 37, 4645–4656 CrossRef CAS.
- R. Pei, S.-C. Kim, K. H. Carlson and A. Pruden, Water Res., 2006, 40, 2427–2435 CrossRef CAS.
- G. S. Bezanson, R. Khakhria, D. Duck and H. Lior, Appl. Environ. Microbiol., 1985, 50, 1279–1284 CAS.
- C. H. Bolster, A. L. Mills, G. M. Hornberger and J. S. Herman, Water Resour. Res., 1999, 35, 1797–1807 CrossRef CAS.
- A. L. Mills, J. S. Herman, G. M. Hornberger and T. H. DEJesus, Appl. Environ. Microbiol., 1994, 60, 3300–3306 CAS.
- D. E. Fontes, A. L. Mills, G. M. Hornberger and J. S. Herman, Appl. Environ. Microbiol., 1991, 57, 2473–2481 CAS.
- U.S. CLSI, Clinical and Laboratory Standards Institute (CLSI)/National Committee for Clinical Laboratory, 2003, vol. 22, p. 107.
- C.-A. D. Burnham, S. E. Shokoples and G. J. Tyrrell, Microbiology, 2007, 153, 4240–4252 CrossRef CAS.
- M. Beanan and S. Strome, Development, 1992, 116, 755–766 CAS.
-
T. Stiernagle, ed., Maintenance of C. elegans, Oxford University Press, Oxford, UK, 2005 Search PubMed.
- S. Brenner, Genetics, 1974, 77, 71–94 CAS.
- A. Aballay, P. Yorgey and F. M. Ausubel, Curr. Biol., 2000, 10, 1539–1542 CrossRef CAS.
- W. Paulander, A. Pennhag, D. I. Andersson and S. Maisnier-Patin, Antimicrob. Agents Chemother., 2006, 51, 766–769 CrossRef.
- J. L. Tenor, B. A. McCormick, F. M. Ausubel and A. Aballay, Curr. Biol., 2004, 14, 1018–1024 CrossRef CAS.
- C. Mouslim, F. Hilbert, H. Huang and E. A. Groisman, Mol. Microbiol., 2002, 45, 1019–1027 CrossRef CAS.
- S. A. Carlson, R. M. Willson, A. J. Crane and K. E. Ferris, Microb. Pathog., 2000, 28, 373–378 CrossRef CAS.
- M. D. Winfield and E. A. Groisman, Appl. Environ. Microbiol., 2003, 69, 3687–3694 CrossRef CAS.
- A. M. McKay, Lett. Appl. Microbiol., 1992, 14, 129–135 CrossRef.
- D. B. Roszak and R. R. Colwell, Microbiol. Mol. Biol. Rev., 1987, 51, 365–379 CAS.
- G. Bogosian and E. V. Bourneuf, EMBO Rep., 2001, 2, 770–774 CrossRef CAS.
- D. B. Roszak and R. R. Colwell, Appl. Environ. Microbiol., 1987, 53, 2889–2893 CAS.
- R. R. Colwell, P. Brayton, D. Herrington, B. Tall, A. Huq and M. M. Levine, World J. Microbiol. Biotechnol., 1996, 12, 28–31 CrossRef.
- D. J. Grimes and R. R. Colwell, FEMS Microbiol. Lett., 1986, 34, 161–165 CrossRef.
- G. J. Mederma, F. M. Schets, A. W. Giessen and A. H. Havelaar, J. Appl. Microbiol., 1992, 72, 512–516 CrossRef.
- B. Baleux, A. Caro, J. Lesne, P. Got, S. Binard and B. Delpeuch, Oceanol. Acta, 1998, 21, 939–950 CrossRef.
-
P. F. McDermott, in Antimicrobial resistance in bacteria of animal origin, ed. F. M. Aarestrup, American Society for Microbiology, Washington, DC, 2006 Search PubMed.
- C. W. Knapp, C. A. Engemann, M. L. Hanson, P. L. Keen, K. J. Hall and D. W. Graham, Environ. Sci. Technol., 2008, 42, 5348–5353 CrossRef CAS.
- A. D. Anderson, J. M. Nelson, S. Rossiter and F. J. Angulo, Microb. Drug Resist., 2003, 9, 373–379 CrossRef CAS.
- W. Witte, Science, 1998, 279, 996 CrossRef CAS.
- S. Thiele-Bruhn, J. Plant Nutr. Soil Sci., 2003, 166, 145–167 CrossRef CAS.
- A. B. A. Boxall, D. W. Kolpin, B. Halling-SÃ,rensen and J. Tolls, Environ. Sci. Technol., 2003, 37, 286A–294A CrossRef CAS.
- B. D. Jones, C. A. Lee and S. Falkow, Infect. Immun., 1992, 60, 2475–2480 CAS.
- J. M. Adaska, A. J. Silva and W. M. Sischo, Vet. Microbiol., 2008, 128, 90–95 CrossRef CAS.
- J. D. Boddicker, N. A. Ledeboer, J. Jagnow, B. D. Jones and S. Clegg, Mol. Microbiol., 2002, 45, 1255–1265 CrossRef CAS.
- A. Bishop, D. House, T. Perkins, S. Baker, R. A. Kingsley and G. Dougan, Microbiology, 2008, 154, 1914–1926 CrossRef CAS.
-
M. Calfie, Wormbook, http://www.wormbook.org/, accessed November 19, 2009 Search PubMed.
- A. Labrousse, S. Chauvet, C. Couillault, C. Léopold Kurz and J. J. Ewbank, Curr. Biol., 2000, 10, 1543–1545 CrossRef CAS.
- A. Aballay and F. M. Ausubel, Proc. Natl. Acad. Sci. U. S. A., 2001, 98, 2735–2739 CrossRef CAS.
- N. V. Gerven, V. Derous and J.-P. Hernalsteens, FEMS Microbiol. Lett., 2008, 278, 236–241 CrossRef.
- J. P. Oza, J. B. Yeh and N. O. Reich, FEMS Microbiol. Lett., 2005, 245, 53–59 CrossRef CAS.
- J. W. Peterson and D. W. Niesel, Rev. Infect. Dis., 1988, 10, S319–S322 CAS.
- D. W. Niesel and J. W. Peterson, FEMS Microbiol. Lett., 1987, 41, 299–304 CrossRef CAS.
- E. G. Vescovi, F. C. Soncini and E. A. Groisman, Cell, 1996, 84, 165–174 CrossRef CAS.
- K. M. Papp-Wallace and M. E. Maguire, J. Bacteriol., 2008, 190, 6509–6516 CrossRef CAS.
- S. V. Spinelli, L. B. Pontel, E. G. Véscovi and F. C. Soncini, FEMS Microbiol. Lett., 2008, 280, 226–234 CrossRef CAS.
- J. Su, H. Gong, J. Lai, A. Main and S. Lu, Infect. Immun., 2008, 77, 667–675 CrossRef.
- A. Caro, P. Got, J. Lesne, S. Binard and B. Baleux, Appl. Environ. Microbiol., 1999, 65, 3229–3232 CAS.
Footnote |
† Electronic supplementary information (ESI) available: Tables S1–S5. See DOI: 10.1039/c1em10723b |
|
This journal is © The Royal Society of Chemistry 2012 |
Click here to see how this site uses Cookies. View our privacy policy here.