Over 6 years, Escherichia coli were isolated from water samples from seven Seine estuary stations, characterized by a densely populated watershed (654 isolates). Resistances of these E. coli to 16 antibiotics were determined and compared with the same resistances in E. coli isolated from a small stream (120 isolates) and from the treated effluent of the largest estuary wastewater treatment plant (123 isolates). Between 30.2% and 56.6% of the estuary isolates were resistant, whatever the station or time of sampling; of these, 60.5-80% were resistant to at least two and up to 12 antibiotics. In the three contrasting sites, resistances to tetracycline, amoxicillin and ticarcillin were the commonest. DNA was extracted from 279 estuary isolates (January 2006) and class 1, 2 and 3 integrons were detected by multiplex real-time PCR and confirmed by classic PCR. IntI1 and intI2 genes were found in 11% of isolates. No intI3 gene was detected. The variable regions of the class 1 and 2 integrons sequenced contained predominantly gene cassettes aadA and dfr. However, for slightly over half of the E. coli isolates exhibiting the class 1 integron, the variable region could not be amplified, because part of the 3' conserved sequence was missing.

Background: Escherichia coli is a commensal bacterium of the gastro-intestinal tract of human and vertebrate animals, although the aquatic environment could be a secondary habitat. The aim of this study was to investigate the effect of hydrological conditions on the structure of the E. coli population in the water of a creek on a small rural watershed in France composed of pasture and with human occupation. Results: It became apparent, after studying the distribution in the four main E. coli phylo-groups (A, B1, B2, D), the presence of the hly (hemolysin) gene and the antibiotic resistance pattern, that the E. coli population structure was modified not only by the hydrological conditions (dry versus wet periods, rainfall events), but also by how the watershed was used (presence or absence of cattle). Isolates of the B1 phylo-group devoid of hly and sensitive to antibiotics were particularly abundant during the dry period. During the wet period and the rainfall events, contamination from human sources was predominantly characterized by strains of the A phylo-group, whereas contamination by cattle mainly involved B1 phylo-group strains resistant to antibiotics and exhibiting hly. As E. coli B1 was the main phylo-group isolated in water, the diversity of 112 E. coli B1 isolates was further investigated by studying uidA alleles (beta-D-glucuronidase), the presence of hly, the O-type, and antibiotic resistance. Among the forty epidemiolgical types (ETs) identified, five E. coli B1 ETs were more abundant in slightly contaminated water.

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Occurrences of antibiotic‐resistant Escherichia coli in two springs of a karstic system (NW France) providing drinking water were determined to study the role of aquifers in the dissemination of the resistance genes. Water samples were collected during wet and dry periods and after a heavy rainfall event to investigate E. coli density, antibiotic resistance patterns, and occurrences of class 1, 2, and 3 integrons. By observing patterns of the resistant isolates (i.e. number and type of resistances) and their occurrences, we were able to define two resistant subpopulations, introduced in the aquifer via surface water: (1) R1‐2, characterized by one or two resistance(s), essentially to chloramphenicol and/or tetracycline (96.5%), was always found during the heavy rainfall event; (2) R3‐10, characterized by three or more resistances, mostly resistant to tetracycline (94.1%) and beta‐lactams (86%), was found transiently. Class 1 and 2 integrons were detected, mostly in the R3‐10 subpopulation for class 1 integrons. The characteristics of these two subpopulations strongly suggest that the contamination originates from pasture runoff for the R1‐2 subpopulation and from wastewater treatment plant effluents for the R3‐10 subpopulation. These two subpopulations of E. coli could be used as biological indicators to determine the origin of groundwater contamination.