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Applied and Environmental Microbiology, August 2008, p. 4966-4968, Vol. 74, No. 15
0099-2240/08/$08.00+0 doi:10.1128/AEM.02900-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.

U.S. Environmental Protection Agency, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Research Triangle Park, North Carolina,1 Centers for Disease Control and Prevention, National Center for HIV, STD, and TB Prevention, Division of TB Elimination, Atlanta, Georgia,2 U.S. Environmental Protection Agency, Office of Research and Development, National Exposure Research Laboratory, Cincinnati, Ohio,3 U.S. Environmental Protection Agency, Region 10 Laboratory, Port Orchard, Washington,4 Clark County Water Reclamation District, Las Vegas, Nevada5
Received 21 December 2007/ Accepted 26 May 2008
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We collaborated with personnel from laboratories that isolate and identify mycobacteria from human specimens collected during patient care activities. We obtained clinical isolates of M. avium complex that were collected from county residents during the study period. We recorded each anatomic site of collection and each patient's residential zip code. The study was approved by and conducted in adherence with the human subjects' requirements of the Institutional Review Board of the University of North Carolina at Chapel Hill.
A subset of viable M. avium complex clinical isolates was selected for molecular analysis using specific selection criteria. Isolates were more likely to be analyzed when they were isolated from a sterile site and the patient's zip code was included in the municipal water distribution area. M. avium complex isolates were identified as either M. avium or Mycobacterium intracellulare using multilocus enzyme electrophoresis (MEE) (11, 12). Isolates identified as M. avium which shared an electrophoretic type (ET) were further subtyped by pulsed-field gel electrophoresis (PFGE) using 40 U of XbaI for each restriction reaction (7). The Tenover criteria were used to evaluate relatedness of PFGE fragment patterns (10).
Groups of related isolates were evaluated to confirm that isolates were collected from unique individuals. If isolates were collected from the same individual or if we could not confirm that the isolates were collected from unique individuals, we retained only the isolate with the earliest collection date from the group.
Twenty-seven M. avium isolates from four drinking-water POU sites were typed using MEE. Among 23 isolates and 4 identical ETs, PFGE was used for greater genetic discrimination, yielding 4 identical or closely related PFGE groups.
We received 253 M. avium complex clinical isolates: 200 (79%) from respiratory sites, 37 (15%) from normally sterile sites, and 16 (6%) from other sites, such as wounds and stool. We analyzed 126 of these using MEE; of these, 88 (70%) were identified as M. avium. Fifty-six of the 88 (64%) M. avium isolates were from respiratory sites, 25 (28%) from normally sterile sites, and 7 (8%) from other sites, such as wounds and stool.
Seventy-four isolates were from patients with a home zip code served by the municipal water system. Among these clinical isolates, we found one that was closely related to an environmental M. avium isolate (Fig. 1); the zip code of the patient's residence was adjacent to the drinking-water sample site, providing an additional geographic association between these isolates. Three other clinical M. avium isolates shared an ET with another M. avium environmental isolate but when compared by PFGE analysis were only possibly related (Fig. 2); there was no apparent geographic relationship among these isolates.
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FIG. 1. Closely related clinical (lane 1) and drinking-water (lane 2) M. avium isolates. Lane 3 contains a 48.5-kb ladder.
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FIG. 2. Possibly related M. avium isolates from drinking water (lane 1) and patients (lanes 2 to 4) all shared an electrophoretic group. Lane 5 contains a 48.5-kb ladder.
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FIG. 3. Groups of indistinguishable M. avium isolates from clinical samples: PFGE groups A to E. Group A, lanes 1 to 4; group B, lanes 5 to 7; group D, lanes 8 and 9; group E, lanes 10 and 11; group C, lanes 12 and 13. Lane 14 contains a 48.5-kb ladder.
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We identified five PFGE groups of indistinguishable clinical isolates that were collected over a 2- to 41-month period. These groups likely represent patients with common environmental sources of M. avium exposure, although specific sources of exposure are unknown. Clusters of M. avium infections sharing a PFGE group have previously been reported among individuals (8), sometimes among those with no identified epidemiologic links (5). Clusters such as these may be attributed to either persistence of a common source of exposure or delayed detection of infection or colonization among patients exposed to a transitory common source of exposure. Either exposure scenario is plausible; M. avium strains are reported to persist at drinking-water POU taps for up to 26 months (4). Diagnosis of M. avium complex infections is frequently missed or delayed, particularly among patients with no commonly recognized risk factors for infection (1). Limitations of the study include the lack of patient-specific information, including exposure history and disease status. We analyzed a convenience sample of clinical isolates; unknown biases associated with identification, collection, and viability may have occurred. Environmental isolates were collected from a limited number of drinking-water sites. It is probable that many more strains of M. avium could be isolated from the millions of POU sites located within the municipal utility's distribution area.
Molecular techniques provide the strongest support to link human M. avium infections and environmental exposures. However, progression of infection may be indolent, isolation of M. avium from environmental samples is difficult, and molecular methods are not widely used. Control of this environmentally transmitted infectious disease will continue to be a challenge until detection of new cases of illness increases, methods to identify and isolate M. avium from environmental samples improve, and methods to link human and environmental strains of M. avium are more widely accessible.
Isolates were purchased through contracts 1D-5128-NAEX, 2D-5783-NAEX, and 2D-6115-NAEX.
The views expressed in this report are those of the individual authors and do not necessarily reflect the views and policies of the U.S. Environmental Protection Agency. Mention of trade names or commercial products does not constitute endorsement or recommendation for use.
Published ahead of print on 6 June 2008. ![]()
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