| Literature DB >> 34965260 |
Mohammed Badrul Amin1, Sumita Rani Saha1, Md Rayhanul Islam1, S M Arefeen Haider1, Muhammed Iqbal Hossain1, A S M Homaun Kabir Chowdhury1, Emily K Rousham2, Mohammad Aminul Islam1,3.
Abstract
Fluro(quinolones) is an important class of antibiotic used widely in both human and veterinary medicine. Resistance to fluro(quinolones) can be acquired by either chromosomal point mutations or plasmid-mediated quinolone resistance (PMQR). There is a lack of studies on the prevalence of PMQR in organisms from environmental sources in Bangladesh. In this study, we investigated the occurrence of PMQR genes in E. coli from various water sources and analysed associations between multi-drug resistance (MDR) and resistance to extended spectrum β-lactam antibiotics. We analysed 300 E. coli isolates from wastewaters of urban live-bird markets (n = 74) and rural households (n = 80), rural ponds (n = 71) and river water samples (n = 75) during 2017-2018. We isolated E. coli by filtering 100 ml of water samples through a 0.2μm cellulose membrane and incubating on mTEC agar media followed by identification of isolated colonies using biochemical tests. We selected one isolate per sample for detection of PMQR genes by multiplex PCR and tested for antibiotic susceptibility by disc diffusion. Clonal relatedness of PMQR-positive isolates was evaluated by enterobacterial repetitive intergenic consensus-PCR (ERIC-PCR). About 66% (n = 199) of E. coli isolates harbored PMQR-genes, predominantly qnrS (82%, n = 164) followed by aac(6')-lb-cr (9%, n = 17), oqxAB (7%, n = 13), qnrB (6%, n = 11) and qepA (4%, n = 8). Around 68% (n = 135) of PMQR-positive isolates were MDR and 92% (n = 183) were extended spectrum β-lactamase (ESBL)-producing of which the proportion of positive samples was 87% (n = 159) for blaCTX-M-1' 34% (n = 62) for blaTEM, 9% (n = 16) for blaOXA-1, blaOXA-47 and blaCMY-2, and 2% (n = 4) for blaSHV. Further, 16% (n = 32) of PMQR-positive isolates were resistant to carbapenems of which 20 isolates carried blaNDM-1. Class 1 integron (int1) was found in 36% (n = 72) of PMQR-positive E. coli isolates. PMQR genes were significantly associated with ESBL phenotypes (p≤0.001). The presence of several PMQR genes were positively associated with ESBL and carbapenemase encoding genes such as qnrS with blaCTXM-1 (p<0.001), qnrB with blaTEM (p<0.001) and blaOXA-1 (p = 0.005), oqxAB and aac(6')-lb-cr with blaSHV and blaOXA-1 (p<0.001), qnrB with blaNDM-1 (p<0.001), aac(6')-lb-cr with blaOXA-47 (p<0.001) and blaNDM-1 (p = 0.002). Further, int1 was found to correlate with qnrB (p<0.001) and qepA (p = 0.011). ERIC-PCR profiles allowed identification of 84 of 199 isolates with 85% matching profiles which were further grouped into 33 clusters. Only 5 clusters had isolates (n = 11) with identical ERIC-PCR profiles suggesting that PMQR-positive E. coli isolates are genetically heterogeneous. Overall, PMQR-positive MDR E. coli were widely distributed in aquatic environments of Bangladesh indicating poor wastewater treatment and highlighting the risk of transmission to humans and animals.Entities:
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Year: 2021 PMID: 34965260 PMCID: PMC8716050 DOI: 10.1371/journal.pone.0261970
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
List of primer sequences used in multiplex PCR for the determination of PMQR determinants.
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| Denaturation | Annealing | Extension | ||||
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| 630 | 94°C for 30 seconds | 63°C for 90 seconds | 72°C for 90 seconds | Ciesielczuk et al., 2013 [ | |
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Prevalence of PMQR genes in E. coli isolates obtained from different aquatic environments.
| Sampling site | Sample Type | Sample number (n) | PMQR positive n (%) | No. (%) of isolates positive for PMQR genes | ||||
|---|---|---|---|---|---|---|---|---|
| Urban | Wastewater | 74 | 45 (61) | 52 (65) | 3 (4) | 4 (5) | 0 | 2 (3) |
| Rural | Wastewater | 80 | 58 (72) | 37 (50) | 4 (5) | 3 (4) | 3 (4) | 4 (5) |
| pond water | 71 | 50 (70) | 45 (90) | 2 (4) | 3 (6) | 2 (4) | 0 | |
| river water | 75 | 46 (61) | 30 (65) | 2 (4) | 3 (7) | 3 (7) | 11 (24) | |
| Total | 300 | 199 (66) | 164 (82) | 11 (6) | 13 (7) | 8 (4) | 17 (9) | |
*R, resistance; n, number.
Occurrence of clinically important antibiotic resistance among PMQR-positive E. coli isolates from aquatic environments in Bangladesh.
| Antibiotic classes | Antibiotics tested | No. (%) of | ||||
|---|---|---|---|---|---|---|
| Urban Wastewater (n = 45) | Rural Wastewater (n = 58) | Rural pond water (n = 50) | Rural river water (n = 46) | |||
| Aminoglycoside | Gentamycin | 18 (40) | 7 (12) | 2 (4) | 15 (33) | |
| Antipseudomonal penicillins plus β-lactamase inhibitors | Piperacillin-Tazobactam | 10 (22) | 8 (14) | 6 (12) | 21 (46) | |
| Cephamycins | Cefoxitin | 44 (98) | 56 (97) | 47 (94) | 44 (96) | 0.654 |
| Extended-spectrum cephalosporins | Cefotaxime | 44 (98) | 56 (97) | 45 (90) | 44 (96) | 0.165 |
| Ceftriaxone | 44 (98) | 56 (97) | 45 (90) | 44 (96) | 0.165 | |
| Ceftazidime | 39 (87) | 47 (81) | 38 (76) | 43 (98) | 0.065 | |
| Cefixime | 43 (96) | 56 (97) | 47 (94) | 44 (96) | 0.838 | |
| Cefepime | 44 (98) | 55 (95) | 45 (90) | 44 (96) | 0.277 | |
| Carbapenem | Ertapenem | 9 (20) | 5 (9) | 6 (12) | 10 (22) | 0.343 |
| Meropenem | 10 (22) | 6 (10) | 7 (14) | 9 (19) | 0.363 | |
| Imipenem | 11 (24) | 8 (14) | 6 (12) | 7 (15) | 0.209 | |
| Fluro(quinolone) | Nalidixic acid | 34 (76) | 23 (40) | 19 (38) | 27 (59) | 0.074 |
| Ciprofloxacin | 34 (76) | 20 (34) | 14 (28) | 26 (57) | ||
| Folate pathway inhibitors | Sulfamethoxazole/trimethoprim | 27 (60) | 15 (26) | 11 (22) | 11 (24) | |
| Nitrofuran | Nitrofurantoin | 9 (20) | 8 (14) | 15 (30) | 20 (43) | |
| Penicillin | Ampicillin | 45 (100) | 58 (100) | 50 (100) | 46 (100) | NA |
| MDR (≥3 Ab classes) | 39 (87) | 32 (55) | 29 (58) | 35 (76) | 0.157 | |
| XDR (All antibiotic classes except two or fewer classes) | 8 (18) | 4 (7) | 2 (4) | 13 (28) | ||
Association of PMQR genes with ESBL, carbapenemase, integrase genes, and MDR and XDR phenotypes in E. coli isolates.
| Characteristics | No. (%) of | ||
|---|---|---|---|
| PMQR positive (n = 199) | PMQR negative (n = 101) | ||
| ESBL | 183 (92) | 74 (73) | p<0.001 |
| | 165 (83) | 51 (50) | p<0.001 |
| | 5 (3) | 1 (1) | 0.668 |
| | 63 (32) | 46 (46) | p<0.05 |
| | 17 (9) | 12 (12) | 0.355 |
| | 16 (8) | 13 (13) | 0.181 |
| Carbapenemase | 32 (16) | 17 (17) | 0.70 |
| | 20 (10) | 16 (16) | 0.145 |
| | 16 (8) | 8 (8) | 0.971 |
| | 0 | 0 | NA |
| Class 1 integron ( | 72 (36) | 40 (40) | 0.562 |
| MDR | 135(68) | 74 (73) | 0.334 |
| XDR | 27 (14) | 20 (20) | 0.160 |
*p values were determined using Chi-square or Fisher’s exact test.
Fig 1Correlation matrix of the presence of PMQR genes with ESBL and carbapenemase and integron (int1) encoding genes in E. coli.
White spaces are not significantly correlated. Blue circles indicated significant positive correlation and red showed significant negative correlation. The size and strength of colour represent the numerical value of the Phi correlation coefficient.
Fig 2Dendrogram generated by BioNumerics software, showing distances calculated by the Dice similarity index of ERIC-PCR banding patterns of E. coli strains isolated from various aquatic samples.
The degree of similarity (%) is shown on the scale. The isolates were considered as phylogenetically related based on 85% similarity in ERIC-PCR banding patterns.