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Applied and Environmental Microbiology logoLink to Applied and Environmental Microbiology
. 2010 Nov 19;77(2):684–687. doi: 10.1128/AEM.01425-10

Integron Prevalence and Diversity in Manured Soil

K G Byrne-Bailey 1,#, W H Gaze 1,*, L Zhang 1, P Kay 2,, A Boxall 2,§, P M Hawkey 3, E M H Wellington 1
PMCID: PMC3020556  PMID: 21097590

Abstract

The levels of integron abundance and diversity in soil amended with pig slurry were studied. Real-time PCR illustrated a significant increase in class 1 integron prevalence after slurry application, with increased prevalence still evident at 10 months after application. Culture-dependent data revealed 10 genera, including putative human pathogens, carrying class 1 and 2 integrons.


Integrons are genetic elements that integrate or excise mobile cassette genes, including those that confer resistance to a wide range of antibiotics (8). Class 1 and 2 integrons are associated with carriage of antibiotic resistance genes in clinically important bacteria, and there is increasing evidence of environmental reservoirs of bacteria carrying these integron classes (9, 10, 18, 19). There is concern that the use of veterinary antibiotics selects for antibiotic-resistant bacteria which, along with antibiotic residues, enter the wider environment via slurry application. The impact of slurry application on environmental reservoirs of antibiotic-resistant bacteria is an important question. This study aimed to investigate the molecular prevalence of class 1 integrons and the diversity of class 1 and 2 integrons in bacteria isolated from pig slurry and from amended clay soils. The study site had a history of long-term application of slurry from tylosin (TY)-fed pigs combined with experimental application of slurry containing sulfachloropyridazine (SCP) and oxytetracycline (OTC). Slurry from tylosin-fed pigs (100 g/ton of feed) was applied to soil annually before the start of the experiment; subsequently, two annual experimental applications were also undertaken, containing 18.85 mg/liter and 2.58 mg/liter of SCP and OTC, respectively. The slurry was applied to the field at the same rate as normal agricultural practice (45,000 liters/ha). Antibiotics were added to model sorption properties in soil and represented real-world concentrations found in pig slurry (4, 5). Slurry was stored for up to 3 months in a holding tank containing a mixture of new and older slurry. Soil samples were taken at several time points over the 2-year experimental period (6).

Over 500 isolates from time points before and after slurry application were screened by PCR for intI1 and intI2 (6). Among these, 14.7% (n = 78) were positive for intI1 and/or intI2, 5.0% (n = 27) carried intI1 only compared to 8.5% (n = 45) for intI2 only, and 1.1% (n = 6) were positive for both intI1 and intI2. Integron prevalence in isolates was dependent on the selective medium used, with the numbers of isolates carrying intI1 being significantly higher under TY selection (9.9%) than under OTC (4.8%), SCP (3.8%), or no selection (3.6%) and intI2 being more prevalent under OTC selection (24.8%) than under TY (5.8%), SCP (5.6%), or no selection (0.0%) (chi-square test for comparisons of two proportions). These data suggest that TY and OTC may select or coselect for class 1 and 2 integrons, respectively, with TY selection most likely to occur in the pig gut or in the slurry holding tank, as it was undetectable in soil cores. Conversely, OTC selection may have occurred in the slurry tank or the soil, where it persists (12). There was no clear trend in integron prevalence in isolates at sample points after antibiotic-amended slurry application in either year of the study (data not shown). The molecular prevalence of intI1 in soils in year 1 was determined by using SYBR green real-time PCR on triplicate DNA extractions at each time point (UltraClean soil DNA kit). PCRs were performed on an Applied Biosystems 7500 Fast system, with the reaction mixtures containing 20 μl 2× power SYBR green PCR master mix (Applied Biosystems), 4 μl primer pairs, 0.4 μl bovine serum albumin (10 mg ml−1), 4 μl template DNA diluted 1:10, and 11.6 μl DNA-free H2O. The final concentration of each primer was 0.9 μM for 16S (16), int1f2 (TCGTGCGTCGCCATACA), and int1r2 (GCTTGTTCTACGGCCGTTTGA). Standard curves for absolute quantification were produced from seeded soil inoculated with serial dilutions of Escherichia coli SK4903 (IncPβ R751 carrying intI1 and qacE) (17). Molecular prevalence was calculated by dividing target gene abundance by 16S rRNA abundance and multiplying by 100. Corrections were made for 16S rRNA and IncPβ R751 copy number (1, 21). Melting curves were checked for specificity of PCR amplification, and template dilution experiments were carried out to check for PCR inhibition.

The molecular prevalence of intI1 was significantly lower in preapplication samples than at days 1, 21, 90, and 289 postapplication, using a chi-square test for comparisons of two proportions (P < 0.0001) (Fig. 1). In the pig slurry spread onto the trial plots, 0.21% of bacteria carried intI1 (unpublished data). In preapplication soils, the intI1 prevalence was 0.0002%, which was similar to its prevalence in other unpolluted soils tested (unpublished data); this increased dramatically to 0.01% immediately after application and then decreased slightly to 0.008% at day 21 and then to approximately 0.003 and 0.004% at days 90 and 289, respectively. intI1 prevalence at later time points was still significantly higher than in preapplication soils, indicating that the impact of slurry application on class 1 integron prevalence was still evident after nearly 10 months. This concurs with evidence of sul1 abundance in manured soils measured using real-time PCR, where a manure effect on abundance was still evident at 61 days postapplication (11). The discrepancy between preapplication soil (which had a history of the addition of slurry from tylosin-fed pigs) and postapplication soil (slurry also containing SCP and OTC) may be due to additional selective pressure exerted by SCP and OTC. In the present study, Enterobacteriaceae spp. carrying intI1 were present in soil leachate samples 164 days after slurry application, again suggesting that integron-positive bacteria, likely to have come from slurry, survived in soil for a considerable length of time.

FIG. 1.

FIG. 1.

Molecular prevalence of intI1 in soil amended with pig slurry. Error bars represent standard errors of the results for three replicate samples (four in preapplication soil); the prevalences are statistically significantly different from one another at all time points (chi-square test, P < 0.0001).

16S rRNA PCR and sequencing (6) revealed that the intI-positive isolates belonged to 10 genera/families (Table 1). The largest number of integrase-positive isolates were Pseudomonas spp., which were the only integron-positive genera present throughout the year, including in preapplication samples. Gram-positive Bacillus spp. and Arthrobacter spp. were also identified, carrying both intI1 and intI2 in pig slurry and in soil leachate at day 164 and day 289 postapplication. Arthrobacter and pseudomonas spp. have previously been isolated from pigsties (2). Aerococcus viridians was only isolated from pig slurry; this species is a pathogen of pigs and humans (15). Psychrobacter spp. were isolated from pig slurry, preapplication soil, and at day 1 postapplication; members of this genus are also opportunistic pathogens of animals and humans. Acinetobacter spp., including A. lwoffi, carrying combinations of the two integrase genes were repeatedly characterized in pig slurry and amended soil at day 1 and 21 but were not isolated at later time points or from preapplication cores; this species is an opportunistic human pathogen that is also found as a commensal in healthy individuals (13). Enterobacteriaceae spp. were isolated at year 1, day 1, and in soil leachate at day 164 (year 1), and Enterococcus spp. were isolated in soil leachate at day 164 only. The majority of integron-bearing genera were isolated postapplication, suggesting that they were introduced via slurry application or were already present in the soil and were selected for by antibiotics contained in applied slurry or resulted from horizontal gene transfer between introduced and indigenous bacteria after slurry application. This correlates with the 50-fold increase in intI1 observed immediately after slurry application. It is clear that some integron-positive genera, including Acinetobacter spp., were only isolated up to day 21, which correlated with a decrease in the molecular prevalence of intI1 after this time point.

TABLE 1.

Summary of intI prevalence and sample identification for each species isolated

Genus as identified by 16S rRNA sequencing No. (%) of intI-positive isolates intI genotype(s) No. of isolates Source(s)a Day of isolation postapplication
Acinetobacter 21 (26.9) intI1 3 AS 1, 21
intI2 16 PS 21
Aerococcus 2 (2.6) intI1 1 PS
intI2 1 PS
Arthrobacter 2 (2.6) intI1 2 AS 289
Bacillus 7 (9.0) intI1 2 SL, AS 164, 289
intI2 5 PS, SL 164
intI1, intI2 1 PS, SL 164
Enterococcus 1 (1.3) intI1, intI2 1 SL 164
Pseudomonas 34 (43.6) intI1 19 P, AS 1, 21, 90
intI2 14 P, AS 1, 21, 90, 240
intI1, intI2 2 AS 21
Psychrobacter 6 (7.7) intI2 5 PS, P, AS 1
intI1, intI2 1 PS
Enterobacteriaceae 2 (2.6) intI2 1 AS 1
intI1, intI2 1 SL 164
Stenotrophomonas 1 (1.3) intI2 1 AS 21
Streptomyces 1 (1.3) intI2 1 AS 1
Unknown 1 (1.3) intI2 1 AS 21
a

PS, pig slurry; P, preapplication soil; SL, soil leachate; AS, amended soil.

Only six intI1-positive isolates contained amplifiable variable regions (18), which contained aadA genes (streptomycin/spectinomycin resistance) (GenBank accession number FJ457611); they included Acinetobacter, Aerococcus, Pseudomonas, and Enterobacteriaceae spp. and Arthrobacter arilaitensis, which also carried an intI1Δ1 gene and a 3′ conserved segment (3′-CS) that included qacEΔ1 and sulI (Fig. 2 A) (7). The latter class 1 integron variable region had 99% similarity at the nucleotide level to a class 1 integron located on the pTet3 plasmid from Corynebacterium glutamicum (20). aadA genes were isolated from pig manure in a previous study that demonstrated strong selective pressure for streptomycin/spectinomycin resistance in pig farming (3). In conjugal transfer experiments, conducted as described by Byrne-Bailey et al. (6), the intI1 and sul1 genes from Arthrobacter arilaitensis transferred into E. coli K-12 CV601 at a frequency of 3.71 × 10−3 (transconjugants per number of donor cells) and into Pseudomonas putida UWC1 at a frequency of 2.98 × 10−3 (transconjugants per number of donor cells), indicating the ability of the mobile genetic element bearing the integron to transfer from a Gram-positive host into Gram-negative recipients.

FIG. 2.

FIG. 2.

(A) Schematic of the class 1 integron fragment sequenced from Arthrobacter arilaitensis (isolate C361). (B) Diagrammatic representation of class 2 integron PCR fragments, approximately 1,500 bp in length, sequenced from a number of intI2-positive isolates. (C) Another class 2 integron structure, similar to that shown in panel B but approximately 2,500 bp in length and with the additional insertion of a dfrA1 gene cassette.

The variable regions between intI2 and orfX were amplified in intI2-positive isolates using primers described by White et al. (22); 4 class 2 integron types were characterized, 10 failed to amplify, and 8 gave a 550-bp sequence containing an intI2 gene. The third class 2 integron type, which gave a 1,560-bp product and was found in six isolates, was Tn7 derived, containing intI2, a sat1 gene cassette for streptothricin resistance, an aadA1 gene cassette, and orfX (Fig. 2B) (GenBank accession number FJ469574). The largest of the four class 2 integron types was found in 28 isolates, representing indigenous and introduced bacteria including Acinetobacter, Enterococcus, Pseudomonas, Psychrobacter, Enterobacteriaceae, Stenotrophomonas, and Streptomyces spp. and uncultured bacterium EBSCPSA-6117, and gave a 2,300-bp sequence containing a trimethoprim resistance gene (dfrA1), streptothricin resistance (sat1), streptomycin resistance (aadA1), and orfX (Fig. 2C) (GenBank accession number FJ492781), an arrangement previously described from E. coli isolated from pig feces (14).

Isolates were tested for resistance against eight antibiotics (6). Isolates bearing class 1 integrons demonstrated resistance to more antibiotics than those carrying class 2 integrons (4.4 as opposed to 3.3, respectively; P = 0.037, analysis of variance). One of the isolates resistant to all eight antibiotics, C506, identified as an Enterobacteriaceae sp., was isolated from soil leachate 164 days after slurry application, demonstrating transport of antibiotic-resistant bacteria of agricultural origin to water catchments.

This study demonstrates that pig slurry-amended soil represents a reservoir of diverse bacterial species carrying class 1 and 2 integrons, with indigenous and introduced bacteria carrying the same integron types. The real-time PCR results demonstrated a significant increase in class 1 integrase prevalence after slurry application, and a significant effect was still observable at day 289 postapplication. The risk of resistance gene transfer from the agricultural environment to the clinic is a matter of controversy. However, it is an accepted fact that farm animals and manure are a source of food- and water-borne human pathogens. It is clear that the same transfer routes will bring the human population into contact with commensal and pathogenic bacteria carrying antibiotic resistance genes that may be further disseminated within the human bacterial flora.

Nucleotide sequence accession numbers.

The DNA sequences described in this study have been deposited in the GenBank database under accession numbers FJ457611, FJ469574, and FJ492781.

Acknowledgments

This work was funded in part by an educational grant from Wyeth Pharmaceutical Company, a BBSRC CASE studentship, and NERC grant NER/A/S/2000/01253.

Many thanks to Ron Skurray for strains used in this study.

Footnotes

Published ahead of print on 19 November 2010.

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