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Densities of mesophilic aeromonads were compared in Virginia freshwater lakes with trophic classifications ranging from mesotrophic to hypereutrophic. Aeromonad concentrations were independent of trophic status and did not correlate statistically with water quality parameters used to measure trophic state (total phosphorus, chlorophyll a and Secchi depth). Bacterial indicators (fecal coliforms and Escherichia coli ) used to assess the public health safety of recreational waters correlated with mesophilic aeromonads only when sewage pollution occurred. Overall ( n = 101–107) there were small negative correlations of aeromonad densities with dissolved oxygen ( r = −0.30, P = r = −0.30, P = 0.05). During frequent sampling from April through October 1991, mean mesophilic aeromonad concentrations ranged from 10 3–4 cells 100 ml −1 with the lowest values measured during mid-summer. Over the course of twelve months, 273 aeromonad isolates were identified as belonging to the following biotypes: A. sobria (54%), A. hydrophila (29%), A. caviae (10%), and undetermined (7%). Seasonally, the frequency of isolation of A. sobria , considered the most pathogenic biotype, increased from 17 to 69% when water temperatures exceeded 20°C in a hypereutrophic lake. These temperatures typically occur during periods of peak recreational usage. Phenotypic characteristics associated with virulence were positive in 70% (hemolysis) and 42% (autoagglutination) of glycerol-stored strains ( n = 85), and in 15% (autoagglutination) of strains immediately processed ( n = 73). S-layer proteins associated with invasiveness were not found in 14 strains which autoagglutinated. To evaluate the public health significance of aeromonads in nutrient enriched lakes, our results demonstrate a need to couple investigations of mesophilic aeromonad ecology with virulence and biotype assessments.

The occurrence of male-specific RNA (FRNA) coliphages, proposed as indicators of enteric viruses, was determined in an estuary subject to nonpoint pollution that included fecal inputs from livestock. A host originally developed for detecting FRNA phages in sewage was applied to water and sediment samples. Phages were enumerated using the host Salmonella typhimurium WG49 containing an Escherichia coli plasmid coding for sex pili, and the female parent strain WG45. FRNA phages and fecal coliforms were enumerated in samples collected seasonally from an estuary and associated feeder streams and densities related to selected environmental parameters. Mean phage densities enumerated on WG49 ranged from < 1 to 50 100 ml−1 water and < 13 to 7200 100 g−1 dry sediment. Examination of 300 phages from estuarine and freshwater samples showed that ⩾ 99% were RNase-resistant, ⩾ 94% were lytic to the female parent salmonella strain (WG45), ⩽ 9% were lytic to male E. coli C3000, and none were lytic to female E. coli C. RNase resistant phages lytic to both salmonella strains were noncontractile flexible tailed phages and those lytic to male salmonella or E. coli hosts were filamentous phages. Electron micrographs of the only RNase-sensitive phage recovered that plaqued only male hosts showed cubic phage particles adsorbed to sex pili. Parallel enumerations of environmental samples on WG45 and WG49 yielded equal or greater phage densities on the former host. Purified phages from these samples were lytic to certain salmonella serovars recovered from the environment but did not cross react with fecal coliform or heterotrophic bacteria isolated from the environment. Although the WG49 host was inappropriate to estuarine and freshwater samples examined because of interference by somatic phages, WG45 and WG49 should be examined as hosts for enumerating salmonella phages. Similarly, the public health significance of somatic phages detected by these hosts should be determined. FRNA phages, with a single exception (1187 samples), were not detected in a condemned shellfish growing area subject to nonpoint pollution. This observation questions the application of FRNA phages as indicators of fecal contamination in waters impacted by diffuse fecal inputs.