Waiting on a mule deer crossing…
The presence of Erwinia carotovora in surface and underground (well) water was studied using filter concentration and anaerobic enrichment techniques. The organism was found in water samples collected at sites in mountainous (over 80 km from potato‐producing regions), transitional (upland) and arable regions every month in 1982 and 1983. Filter concentration and anaerobic enrichment of 3‐10 1 of water yielded E. carotovora from 82.8% of the water samples collected from streams, canals and lakes. The organism was detected by direct enrichment of 50 ml water samples in 56.3% of surface water samples collected. Erwinia carotovora subsp. carotovora was the predominant subspecies isolated. Of 1029 strains, 999 (97.1%) were identified as E. carotovora subsp. carotovora and 30 (2.9%) as E. carotovora subsp. atroseptica. Erwinia carotovora subsp. atroseptica was found primarily in water samples collected in arable regions during spring months. Erwinia chrysanthemi was never isolated. Quantitative bacteriological methods were used in 1982 and 1983 to monitor populations of E. carotovora in two streams in south central Colorado. These ranged from undetectable levels to 8.5 cfu/ml of water in Rio Grande River and Saguache Creek. Maximum populations were usually reached by August or September in both streams in both years. Erwinia carotovora was isolated from well water samples collected in the San Luis Valley, but only 15.6 and 15.4% of the samples yielded the organism during 1982 and 1983, respectively. Erwinia carotovora subsp. atroseptica was found only once, and E. carotovora subsp. carotovora was the predominant subspecies detected. Filter concentration of 3.4‐10.0 1 of water plus anaerobic enrichment of the samples was usually necessary to detect E. carotovora in well water.
Items connected by shared entities, co-authorship, citations, or semantic similarity.