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1.
Lett Appl Microbiol ; 49(4): 478-83, 2009 Oct.
Article in English | MEDLINE | ID: mdl-19708885

ABSTRACT

AIMS: Escherichia coli is the faecal indicator species recommended by the US Environmental Protection Agency (USEPA) for monitoring fresh recreational water. Viable but nonculturable (VBNC) E. coli are living cells that are dormant and not culturable using standard microbiological cultivation methods. This study reports a comparison between the mTEC culture method recommended by USEPA for E. coli enumeration and a fluorescent antibody-direct viable count (FA-DVC) method to visualize living E. coli cells with a microscope. METHODS AND RESULTS: Escherichia coli, faecal coliforms and Enterococcus were detected using standard methods recommended by the USEPA. VBNC E. coli was visualized with FA-DVC. Results were analysed with standard statistical methods (Pearson correlation; paired-sample t-test). Significantly higher numbers of E. coli were detected using the FA-DVC method than using the mTEC method. Escherichia coli results were also compared with faecal coliform (mFC broth) and Enterococcus (mEI agar) counts in the same samples. CONCLUSIONS: The results of this comparative study demonstrate that E. coli can be present in higher numbers than what are detected with standard culture methods. SIGNIFICANCE AND IMPACT OF THE STUDY: This study re-emphasizes the need for a rapid, accurate and precise method for detecting health risks to humans who use recreational waters.


Subject(s)
Colony Count, Microbial/methods , Escherichia coli/isolation & purification , Fluorescent Antibody Technique, Direct/methods , Microbial Viability , Seawater/microbiology , Escherichia coli/growth & development
2.
Nat Toxins ; 7(4): 157-65, 1999.
Article in English | MEDLINE | ID: mdl-10797644

ABSTRACT

In October of 1996, a Gymnodinium breve bloom occurred in shellfish harvesting waters of Alabama, Mississippi and Louisiana, Gulf of Mexico, USA. Bloom densities reached 5.6x10(5) cells liter(-1) and bloom residence at shellfish sampling stations ranged from 3 to 28 days. Brevetoxin-2 dominated G. breve toxin profiles in bloom seawater extracts. Shellfish toxicity, assessed by mouse bioassay, exceeded the guidance level for up to 75 days after the bloom had dissipated. Cytotoxicity assays and mouse bioassays showed similar temporal patterns of shellfish toxicity, but the two methods differed in estimations of brevetoxin-3 equivalent toxicity by a factor of 93 to 1. LC-ESI-MS showed the temporal patterns in shellfish toxicity reflected metabolism of G. breve toxins. The molecular ions m/z 1004, 1017 and 1033 dominated LC-ESI-MS spectra of toxic chromatographic fractions from the extracts and were identified as brevetoxin metabolites on the basis of LC-APCI-MS-MS. The discrepancy between cytotoxicity and mouse bioassay estimates of brevetoxin-3 equivalent toxicity resulted from the difference in extraction efficiency of solvents used in the respective methods and the relative sensitivity of the assays to toxin metabolite mixtures present in the extracts. The normalized cytotoxicity assay showed 75% agreement with mouse bioassay positive test samples and 64% agreement with mouse bioassay negative test samples. Published in 1999 by John Wiley & Sons, Ltd.


Subject(s)
Dinoflagellida/chemistry , Marine Toxins/analysis , Ostreidae/chemistry , Oxocins , Sodium Channels/drug effects , Animals , Biological Assay , Brain Neoplasms/pathology , Cell Line , Cell Survival/drug effects , Chromatography, High Pressure Liquid , Marine Toxins/toxicity , Mass Spectrometry , Mice , Neuroblastoma/pathology , Seawater/chemistry , Time Factors
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