Distribution and survival of motile Aeromonas spp. in brackish water receiving sewage treatment effluent
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| Published in | Applied and Environmental Microbiology Vol. 57; no. 9; pp. 2459 - 2467 |
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| Format | Journal Article |
| Language | English |
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American Society for Microbiology
01.09.1991
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| ISSN | 0099-2240 1098-5336 |
| DOI | 10.1128/aem.57.9.2459-2467.1991 |
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The spatiotemporal distributions of Aeromonas spp. and fecal coliforms in a cove receiving sewage treatment effluent and draining into a brackish lagoon were studied for 34 months with sampling at six stations. A total of 452 strains of Aeromonas spp. were isolated and identified at the outflow of the treatment system and at stations in the cove. Hemolytic activity of 289 Aeromonas strains was determined. The Aeromonas spp. and fecal coliform distributions showed seasonal cycles in the pond effluent. These seasonal bacterial cycles were persistent in effluent, at the discharge point, and in the cove. However, the abundance levels of these bacterial distributions decreased gradually from the coast to the open lagoon. A dilution model showed that the Aeromonas spp. and fecal coliform distributions in the cove water were subject not only to dilution effect but also to other environmental factors, such as salinity. A. sobria is the most common species identified in the Aeromonas population present in the cove water. Survival studies confirmed that Aeromonas spp., especially A. sobria, were more sensitive to saline and/or marine stress than fecal coliforms. Among the Aeromonas hydrophila and A. sobria strains, 96 and 97%, respectively, produced hemolysin, whereas among the Aeromonas caviae strains, 95% were nonhemolytic. The spatiotemporal distributions of Aeromonas spp. and fecal coliforms in a cove receiving sewage treatment effluent and draining into a brackish lagoon were studied for 34 months with sampling at six stations. A total of 452 strains of Aeromonas spp. were isolated and identified at the outflow of the treatment system and at stations in the cove. Hemolytic activity of 289 Aeromonas strains was determined. The Aeromonas spp. and fecal coliform distributions showed seasonal cycles in the pond effluent. These seasonal bacterial cycles were persistent in effluent, at the discharge point, and in the cove. However, the abundance levels of these bacterial distributions decreased gradually from the coast to the open lagoon. A dilution model showed that the Aeromonas spp. and fecal coliform distributions in the cove water were subject not only to dilution effect but also to other environmental factors, such as salinity. A. sobria is the most common species identified in the Aeromonas population present in the cove water. Survival studies confirmed that Aeromonas spp., especially A. sobria, were more sensitive to saline and/or marine stress than fecal coliforms. Among the Aeromonas hydrophila and A. sobria strains, 96 and 97%, respectively, produced hemolysin, whereas among the Aeromonas caviae strains, 95% were nonhemolytic.The spatiotemporal distributions of Aeromonas spp. and fecal coliforms in a cove receiving sewage treatment effluent and draining into a brackish lagoon were studied for 34 months with sampling at six stations. A total of 452 strains of Aeromonas spp. were isolated and identified at the outflow of the treatment system and at stations in the cove. Hemolytic activity of 289 Aeromonas strains was determined. The Aeromonas spp. and fecal coliform distributions showed seasonal cycles in the pond effluent. These seasonal bacterial cycles were persistent in effluent, at the discharge point, and in the cove. However, the abundance levels of these bacterial distributions decreased gradually from the coast to the open lagoon. A dilution model showed that the Aeromonas spp. and fecal coliform distributions in the cove water were subject not only to dilution effect but also to other environmental factors, such as salinity. A. sobria is the most common species identified in the Aeromonas population present in the cove water. Survival studies confirmed that Aeromonas spp., especially A. sobria, were more sensitive to saline and/or marine stress than fecal coliforms. Among the Aeromonas hydrophila and A. sobria strains, 96 and 97%, respectively, produced hemolysin, whereas among the Aeromonas caviae strains, 95% were nonhemolytic. Between October 1984 and July 1987, monthly water samples were taken at 6 stations sited near the outflow of a sewage treatment system discharging into a brackish lagoon in southern France. Bacteria were isolated on agar plates; Aeromonas spp. and faecal coliforms were enumerated. Survival of the bacteria under conditions of fast or slow mixing of effluent with lagoon water was studied in diffusion chambers. Analyses of the spatiotemporal distribution of bacteria utilized techniques of chronological clustering, contingency periodograms, time series analyses and kriging. Distributions showed seasonal cycles in the effluent and discharge channel which persisted as far as the discharge point, but faded with distance from this point. Abundance of Aeromonas declined faster than predicted by a dilution model. Aeromonads were more sensitive to saline and/or marine stress than were faecal coliforms; A. sobria, the dominant aeromonad in the lagoon, was particularly sensitive. After 90 d in brackish water, A. sobria cells were still present, but were non-culturable. There are 48 references. The spatiotemporal distributions of Aeromonas spp. and fecal coliforms in a cove receiving sewage treatment effluent and draining into a brackish lagoon were studied for 34 mo with sampling at 6 stations. A total of 452 strains of Aeromonas spp. were isolated and identified at the outflow of the treatment system and at stations in the cove. Hemolytic activity of 289 Aeromonas strains was determined. The Aeromonas spp. and fecal coliform distributions showed seasonal cycles in the pond effluent. These seasonal bacterial cycles were persistent in effluent, at the discharge point, and in the cove. However, the abundance levels of these bacterial distributions decreased gradually from the coast to the open lagoon. A dilution model showed that the Aeromonas spp. and fecal coliform distributions in the cove water were subject not only to dilution effect but also to other environmental factors, such as salinity. |
| Author | P Monfort B Baleux |
| AuthorAffiliation | Unité de Recherche Associée 1355, Université des Sciences et Techniques du Languedoc, Montpellier, France |
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| Keywords | Brackish water environment Aeromonas Bacteria Vibrionaceae Localization Survival Effluent Sewage treatment plant |
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| References_xml | – reference: 500794 - J Clin Microbiol. 1979 Jul;10(1):46-9 – reference: 5635458 - N Engl J Med. 1968 Feb 1;278(5):245-9 – reference: 458841 - J Med Microbiol. 1979 May;12(2):229-31 – reference: 2389929 - Appl Environ Microbiol. 1990 Jul;56(7):1999-2006 – reference: 3055195 - Rev Infect Dis. 1988 Sep-Oct;10(5):980-97 – reference: 3888508 - Diagn Microbiol Infect Dis. 1985 May;3(3):223-32 – reference: 6112237 - J Clin Microbiol. 1981 Apr;13(4):769-77 – reference: 3958147 - J Clin Microbiol. 1986 Mar;23(3):595-9 – reference: 6690467 - J Clin Microbiol. 1984 Jan;19(1):44-7 – reference: 457260 - Infect Immun. 1979 Mar;23(3):829-37 – reference: 31839 - Appl Environ Microbiol. 1978 Nov;36(5):731-8 – reference: 3743554 - Eur J Clin Microbiol. 1986 Jun;5(3):311-6 – reference: 6385848 - Appl Environ Microbiol. 1984 Aug;48(2):361-6 – reference: 566433 - Nouv Presse Med. 1978 Apr 8;7(14):1206-7 – reference: 7396482 - Appl Environ Microbiol. 1980 May;39(5):1010-8 – reference: 3144424 - C R Acad Sci III. 1988;307(9):523-7 – reference: 327932 - Appl Environ Microbiol. 1977 May;33(5):1225-8 – reference: 2877008 - J Clin Microbiol. 1986 Nov;24(5):827-34 – reference: 6232567 - Presse Med. 1984 May 5;13(19):1203-5 – reference: 6972468 - Lab Anim Sci. 1981 Apr;31(2):166-9 – reference: 6643669 - J Clin Microbiol. 1983 Nov;18(5):1196-200 – reference: 3160041 - Presse Med. 1985 Jun 8;14(23):1292 – reference: 4019741 - J Clin Microbiol. 1985 Jul;22(1):48-51 – reference: 3693537 - J Clin Microbiol. 1987 Nov;25(11):2044-8 – reference: 6497372 - Appl Environ Microbiol. 1984 Sep;48(3):586-93 – reference: 6699147 - J Clin Microbiol. 1984 Feb;19(2):175-80 – reference: 7251516 - J Appl Bacteriol. 1981 Apr;50(2):359-77 – reference: 2955380 - Presse Med. 1987 Jun 27;16(25):1244 – reference: 6480102 - Infect Immun. 1984 Oct;46(1):122-7 – reference: 7056580 - Infect Immun. 1982 Feb;35(2):666-73 – reference: 2068383 - Res Microbiol. 1991 Jan;142(1):95-102 – reference: 1154921 - Zentralbl Bakteriol Orig B. 1975 May;160(3):237-45 – reference: 3540304 - J Med Microbiol. 1986 Dec;22(4):303-9 – reference: 102785 - J Protozool. 1978 Aug;25(3 Pt 2):351-5 |
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Reddit... The spatiotemporal distributions of Aeromonas spp. and fecal coliforms in a cove receiving sewage treatment effluent and draining into a brackish lagoon were... Between October 1984 and July 1987, monthly water samples were taken at 6 stations sited near the outflow of a sewage treatment system discharging into a... |
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| SubjectTerms | Aeromonas Aeromonas - growth & development Aeromonas - isolation & purification Aeromonas caviae Aeromonas hydrophila Aeromonas sobria Biological and medical sciences Brackish Drainage, Sanitary Enterobacteriaceae - growth & development Enterobacteriaceae - isolation & purification Feces - microbiology Fundamental and applied biological sciences. Psychology Microbiology Sewage Water Microbiology |
| Title | Distribution and survival of motile Aeromonas spp. in brackish water receiving sewage treatment effluent |
| URI | http://aem.asm.org/content/57/9/2459.abstract https://www.ncbi.nlm.nih.gov/pubmed/1768120 https://www.proquest.com/docview/13727688 https://www.proquest.com/docview/16094512 https://www.proquest.com/docview/72617343 https://pubmed.ncbi.nlm.nih.gov/PMC183603 |
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