Enumeration of viable E. coli in rivers and wastewaters by fluorescent in situ hybridization

A combination of direct viable count (DVC) and fluorescent in situ hybridization (FISH) procedures was used to enumerate viable Escherichia coli in river waters and wastewaters. A probe specific for the 16S rRNA of E. coli labeled with the CY3 dye was used; enumeration of hybridized cells was performed by epifluorescence microscopy. Data showed that the method was able to accurately enumerate a minimum of 3000 viable E. coli among a large number of non-fecal bacteria. When applied to river water and wastewater samples, the DVC-FISH method gave systematically higher E. coli counts than a reference culture-based method (miniaturized MPN method). The ratio between both counts (DVC-FISH/MPN) increased with decreasing abundance of culturable E. coli indicating that the proportion of viable but non-culturable (VBNC) E. coli (detectable by the DVC-FISH procedure and not by a culture-based method) was higher in low contaminated environments. We hypothesized that the more stressing conditions, i.e. nutritional stress and sunlight effect, met in low contaminated environments were responsible for the larger fraction of VBNC E. coli. A survival experiment, in which sterile mineral water was inoculated with a pure E. coli strain and incubated, confirmed that stressing conditions induced the apparition of non-culturable E. coli detectable by the DVC-FISH procedure. The analysis of the E. coli concentration along a Seine river longitudinal profile downstream a large input of fecal bacteria by a WWTP outfall showed an increasing fraction of VBNC E. coli with increasing residence time of the E. coli in the river after release. These data suggest that the DVC-FISH method is useful tool to analyze the dynamics of fecal bacteria in river water.     

Use of a commercial gene probe assay kit for rapid MPN enumeration of Escherichia coli in drinking water

A commercial gene probe assay kit for presence/absence determination of Escherichia coli in food samples has been used in the standard UK six tube format most probable number (MPN) method for enumerating E. coli in drinking water samples. Presence/absence analysis with the gene probe kit (requiring 3 h) of all MPN tubes after a 21–24 h incubation (minerals modified glutamate; 37°C) enumerated confirmed E. coli in 24–27 h which offered an improvement of up to 48 h over the standard UK MPN method. MPNs determined by the gene probe method and the standard UK method agreed in nine of the 16 water samples which were analysed and for which E. coli concentrations were within the detection limits of the six tube MPN format. This was consistent with the gene probe method detecting one E. coli in a tube. For the other seven water samples, the gene probe method registered positive only 20 of the 30 tubes which the standard UK method determined to be positive. The sensitivity of the gene probe method for drinking water samples, although encouraging, needs improvement perhaps through kit quality control procedures.     

Comparison of the recoveries of Escherichia coli and total coliforms from drinking water by the MI agar method and the U.S. Environmental Protection Agency-approved membrane filter method.

Drinking water regulations under the Final Coliform Rule require that total coliform-positive drinking water samples be examined for the presence of Escherichia coli or fecal coliforms. The current U.S. Environmental Protection Agency-approved membrane filter (MF) method for E. coli requires two media, an MF transfer, and a total incubation time of 28 h. A newly developed MF method, the MI agar method, containing indoxyl-beta-D-glucuronide and 4-methylumbelliferyl-beta-D-galactopyranoside for the simultaneous detection of E. coli and total coliforms, respectively, by means of their specific enzyme reactions, was compared with the approved method by the use of wastewater-spiked tap water samples. Overall, weighted analysis of variance (significance level, 0.05) showed that the new medium recoveries of total coliforms and E. coli were significantly higher than those of mEndo agar and nutrient agar plus MUG (4-methylumbelliferyl-beta-D-glucuronide), respectively, and the background counts were significantly lower than those of mEndo agar (< 5%). Generally, the tap water source, overall chlorine level, wastewater source, granular activated carbon treatment of the tap water, and method of grouping data by E. coli count for statistical analysis did not affect the performance of the new medium.     

SYBR green real time-polymerase chain reaction as a rapid and alternative assay for the efficient identification of all existing Escherichia coli biotypes approved directly in wastewater samples

Escherichia coli has been recognized as the principal indicator of fecal contamination of water. Indeed, E. coli is the only species in the coliform group found in relationship with gastrointestinal tract of human and warm‐blooded animals and subsequently excreted in large numbers in the human feces. To obtain a complete picture of water quality and therefore, a better protection of public health, different techniques for water analysis have been proposed. In this article, we describe an alternative method that uses SYBR green real time‐polymerase chain reaction (RT‐PCR) technology to identify and quantify all E. coli biotypes in a group of wastewater samples collected from a wastewater depurator located in South of Italy. This new RT‐PCR protocol is accurate in measuring the concentration of chromosomal E. coli DNA using the amplification of three new specific fragments of the following bacteria genes: CadC, HNS, and Allan whose sequence is specific for E. coli family and conserved in all E. coli subtypes. This method allowed us to detect the presence of all E. coli biotypes directly in wastewater samples and estimated the correspondence between colony forming units and bacterial DNA concentrations. The availability of a rapid and sensitive method may be useful to monitor the persistence of E. coli in water, to evaluate the efficiency of wastewater purification treatments and the possible recycle for agricultural use. Furthermore, the development of a simple and routine method to monitor water quality with RT‐PCR analysis can encourage the testing of a higher number of samples. © 2012 American Institute of Chemical Engineers Biotechnol. Prog., 28: 1106–1113, 2012     

Effect of oxygen on survival of faecal pollution indicators in drinking water

AIMS: The aim of this study was to determine the effect of oxygen on the survival of faecal pollution indicators including Escherichia coli in nondisinfected drinking water. METHODS AND RESULTS: Aerobic and anaerobic drinking water microcosms were inoculated with E. coli ATCC 25922 or raw sewage. Survival of E. coli was monitored by membrane filtration combined with cultivation on standard media, and by in situ hybridization with 16S rRNA-targeted fluorescent oligonucleotide probes. Anaerobic conditions significantly increased the survival of E. coli in drinking water compared with aerobic conditions. Escherichia coli ATCC 25922 showed a biphasic decrease in survival under aerobic conditions with an initial first-order decay rate of -0.11 day(-1) followed by a more rapid rate of -0.35 day(-1). In contrast, the first-order decay rate under anaerobic conditions was only -0.02 day(-1). After 35 days, <0.01% of the initial E. coli ATCC 25922 population remained detectable in aerobic microcosms compared with 48% in anaerobic microcosms. A poor survival was observed under aerobic conditions regardless of whether E. coli ATCC 25922 or sewage-derived E. coli was examined, and regardless of the detection method used (CFU or fluorescent in situ hybridization). Aerobic conditions in drinking water also appeared to decrease the survival of faecal enterococci, somatic coliphages and coliforms other than E. coli. CONCLUSIONS: The results indicate that oxygen is a major regulator of the survival of E. coli in nondisinfected drinking water. The results also suggest that faecal pollution indicators other than E. coli may persist longer in drinking water under anaerobic conditions. SIGNIFICANCE AND IMPACT OF THE STUDY: The effect of oxygen should be considered when evaluating the survival potential of enteric pathogens in oligotrophic environments.     

Assessment of the effects of holding time and temperature on Escherichia coli densities in surface water samples

Escherichia coli is a routinely used microbiological indicator of water quality. To determine whether holding time and storage conditions had an effect on E. coli densities in surface water, studies were conducted in three phases, encompassing 24 sites across the United States and four commonly used monitoring methods. During all three phases of the study, E. coli samples were analyzed at time 0 and at 8, 24, 30, and 48 h after sample collection. During phase 1, when 4 degrees C samples were evaluated by Colilert or by placing a membrane onto mFC medium followed by transfer to nutrient agar containing 4-methylumbelliferyl-beta-D-glucuronide (mFC/NA-MUG), three of four sites showed no significant differences throughout the 48-h study. During phase 2, five of seven sites showed no significant difference between time 0 and 24 h by membrane filtration (mFC/NA-MUG). When evaluated by the Colilert method, five of seven sites showed no significant difference in E. coli density between time 0 and 48 h. During phase 3, 8 of 13 sites showed no significant differences in E. coli densities between time 0 and the 48-h holding time, regardless of method. Based on the results of these studies, it appears that if samples are held below 10 degrees C and are not allowed to freeze, most surface water E. coli samples analyzed by commonly used methods beyond 8 h after sample collection can generate E. coli data comparable to those generated within 8 h of sample collection. Notwithstanding this conclusion, E. coli samples collected from surface waters should always be analyzed as soon as possible.     

Detection of Escherichia coli with fluorescent labeled phages that have a broad host range to E. coli in sewage water

Escherichia coli is used as an indicator microorganism in public health. The conventional way to detect E. coli requires several days to produce a result, because it requires incubation of cells. Therefore a rapid and sensitive detection method is needed. T4e-/GFP phage, characterized by suppression of lysozyme and fusion of GFP (green fluorescent protein) to its SOC (small outer capsid) protein, was constructed, and it was shown to be able to detect E. coli K12 sensitively within several hours. However, because the host range of T4 phage to E. coli present in sewage water and sea water is narrow, this phage cannot be used to detect E. coli in environmental water. Two phages named IP008 and IP052, which have a broad host range to E. coli present in sewage influent, were screened from sewage influent. Mixture of these two phages produced clear plaques on 50% of E. coli screened from sewage influent. To use these phages as a tool for detection of E. coli, gfp was inserted into gene e, which encodes a lytic enzyme, and thus lytic-activity-suppressed phages were constructed (IP008e-/GFP and IP052e-/GFP). However, the fluorescent intensity of E. coli cells infected with IP008e-/GFP and IP052e-/GFP was not enough for visualization of the cell. Therefore, in addition to the insertion of gfp into gene e, fusion of GFP to SOC of IP008e-/GFP and IP052e-/GFP was conducted to produce IP008e-/2xGFP and IP052e-/2xGFP. E. coli cells infected with IP008e-/2xGFP and IP052e-/2xGFP showed much stronger fluorescence intensity than E. coli cells infected by IP008e-/GFP and IP052e-/GFP. It is anticipated that, using these GFP-labeled phages, a broad range of E. coli present in sewage influent water can be detected rapidly.     

Evaluation of a rapid, defined substrate technology method for enumeration of total coliforms and Escherichia coli in chlorinated drinking water

A rapid, defined substrate technology method, commercially available as Colilert, simultaneously enumerates total coliforms and Escherichia coli in drinking water samples in 24 h without the need for confirmatory tests. The ability of this method to enumerate both total coliforms and E. coli in simulated chlorine-treated drinking water samples was compared with the standard UK method (minerals-modified glutamate most probable number) which requires up to 96 h to complete including confirmation. Statistical analysis by a nonparametric matched-pair test showed the Colilert method to be less efficient at detecting down to one E. coli in these samples compared to the standard UK method. No statistically significant difference between the two methods of enumeration for total coliforms was detected.     

Direct detection by polymerase chain reaction (PCR) of Escherichia coli in water and soft cheese and identification of enterotoxigenic strains

PCR was used to develop a method to detect Escherichia coli in surface water and soft cheese, which does not require cultivation of bacteria. DNA sequences from the ma /B operon of E. coli were amplified to specifically detect this bacterium. Samples of surface water and soft cheese naturally contaminated with E. coli from less than 100 cells per g up to several times 10⁵cells per g were analysed by both the classical culture method and the PCR assay. Comparable results were obtained with both methods. Soft cheese samples artificially contaminated with various levels of enterotoxigenic E. coli were analysed with a second PCR test specific for the heat-labile enterotoxin type I (LTI) of E. coli. The detection limit was about 1000 bacteria per g of soft cheese. In addition, two soft cheese samples naturally contaminated with 2 times 10⁵and 6 times 10⁵ E. coli per g as determined by the culture method were analysed by LTI-PCR and found to contain low levels of enterotoxigenic E. coli.     

Detection of coliform bacteria in water by polymerase chain reaction and gene probes.

Polymerase chain reaction (PCR) amplification and gene probe detection of regions of two genes, lacZ and lamB, were tested for their abilities to detect coliform bacteria. Amplification of a segment of the coding region of Escherichia coli lacZ by using a PCR primer annealing temperature of 50 degrees C detected E. coli and other coliform bacteria (including Shigella spp.) but not Salmonella spp. and noncoliform bacteria. Amplification of a region of E. coli lamB by using a primer annealing temperature of 50 degrees C selectively detected E. coli and Salmonella and Shigella spp. PCR amplification and radiolabeled gene probes detected as little as 1 to 10 fg of genomic E. coli DNA and as a few as 1 to 5 viable E. coli cells in 100 ml of water. PCR amplification of lacZ and lamB provides a basis for a method to detect indicators of fecal contamination of water, and amplification of lamB in particular permits detection of E. coli and enteric pathogens (Salmonella and Shigella spp.) with the necessary specificity and sensitivity for monitoring the bacteriological quality of water so as to ensure the safety of water supplies.     

Examination of the watershed-wide distribution of Escherichia coli along Southern Lake Michigan: an integrated approach

Recent research has highlighted the occurrence of Escherichia coli in natural habitats not directly influenced by sewage inputs. Most studies on E. coli in recreational water typically focus on discernible sources (e.g., effluent discharge and runoff) and fall short of integrating riparian, nearshore, onshore, and outfall sources. An integrated "beachshed" approach that links E. coli inputs and interactions would be helpful to understand the difference between background loading and sewage pollution; to develop more accurate predictive models; and to understand the differences between potential, net, and apparent culturable E. coli. The objective of this study was to examine the interrelatedness of E. coli occurrence from various coastal watershed components along southern Lake Michigan. The study shows that once established in forest soil, E. coli can persist throughout the year, potentially acting as a continuous non-point source of E. coli to nearby streams. Year-round background stream loading of E. coli can influence beach water quality. E. coli is present in highly variable counts in beach sand to depths just below the water table and to distances at least 5 m inland from the shore, providing a large potential area of input to beach water. In summary, E. coli in the fluvial-lacustrine system may be stored in forest soils, sediments surrounding springs, bank seeps, stream margins and pools, foreshore sand, and surface groundwater. While rainfall events may increase E. coli counts in the foreshore sand and lake water, concentrations quickly decline to prerain concentrations. Onshore winds cause an increase in E. coli in shallow nearshore water, likely resulting from resuspension of E. coli-laden beach sand. When examining indicator bacteria source, flux, and context, the entire "beachshed" as a dynamic interacting system should be considered.     

Detection of Escherichia coli in biofilms from pipe samples and coupons in drinking water distribution networks

Fluorescence in situ hybridization (FISH) was used for direct detection of Escherichia coli on pipe surfaces and coupons in drinking water distribution networks. Old cast iron main pipes were removed from water distribution networks in France, England, Portugal, and Latvia, and E. coli was analyzed in the biofilm. In addition, 44 flat coupons made of cast iron, polyvinyl chloride, or stainless steel were placed into and continuously exposed to water on 15 locations of 6 distribution networks in France and Latvia and examined after 1 to 6 months exposure to the drinking water. In order to increase the signal intensity, a peptide nucleic acid (PNA) 15-mer probe was used in the FISH screening for the presence or absence of E. coli on the surface of pipes and coupons, thus reducing occasional problems of autofluorescence and low fluorescence of the labeled bacteria. For comparison, cells were removed from the surfaces and examined with culture-based or enzymatic (detection of beta-d-glucuronidase) methods. An additional verification was made by using PCR. Culture method indicated presence of E. coli in one of five pipes, whereas all pipes were positive with the FISH methods. E. coli was detected in 56% of the coupons using PNA FISH, but no E. coli was detected using culture or enzymatic methods. PCR analyses confirmed the presence of E. coli in samples that were negative according to culture-based and enzymatic methods. The viability of E. coli cells in the samples was demonstrated by the cell elongation after resuscitation in low-nutrient medium supplemented with pipemidic acid, suggesting that the cells were present in an active but nonculturable state, unable to grow on agar media. E. coli contributed to ca. 0.001 to 0.1% of the total bacterial number in the samples. The presence and number of E. coli did not correlate with any of physical and/or chemical characteristic of the drinking water (e.g., temperature, chlorine, or biodegradable organic matter concentration). We show here that E. coli is present in the biofilms of drinking water networks in Europe. Some of the cells are metabolically active but are often not detected due to limitations of traditionally used culture-based methods, indicating that biofilm should be considered as a reservoir that must be investigated further in order to evaluate the risk for human health.     

Comparative study of commercial 4-methylumbelliferyl-beta-D-glucuronide preparations with the Standard Methods membrane filtration fecal coliform test for the detection of Escherichia coli in water samples.

The performance capabilities of two commercial 4-methylumbelliferyl-beta-D-glucuronide preparations were evaluated for the detection of Escherichia coli from water samples. Eighty-three water samples were collected from a treated water reservoir, and 32 samples were collected from untreated surface water. There was a statistically significant difference between the two commercial preparations compared with the Standard Methods membrane filtration fecal coliform (MFC) method for the detection of E. coli from treated water samples. However, there was no difference between the two methods and the MFC test for E. coli detection from the untreated surface water samples. The disagreement between the two commercial products and the MFC method was primarily due to the occurrence of false-negative results with the two commercial products. The data indicate that the occurrence of false-negative samples could be attributed to impaired substrate specificity and sensitivity of the two tests for E. coli detection. There was no apparent relationship between the occurrence of false-negative results and heterotrophic plate counts in samples.     

Detection of coliform bacteria in water by polymerase chain reaction and gene probes

Polymerase chain reaction (PCR) amplification and gene probe detection of regions of two genes, lacZ and lamB, were tested for their abilities to detect coliform bacteria. Amplification of a segment of the coding region of Escherichia coli lacZ by using a PCR primer annealing temperature of 50 degrees C detected E. coli and other coliform bacteria (including Shigella spp.) but not Salmonella spp. and noncoliform bacteria. Amplification of a region of E. coli lamB by using a primer annealing temperature of 50 degrees C selectively detected E. coli and Salmonella and Shigella spp. PCR amplification and radiolabeled gene probes detected as little as 1 to 10 fg of genomic E. coli DNA and as a few as 1 to 5 viable E. coli cells in 100 ml of water. PCR amplification of lacZ and lamB provides a basis for a method to detect indicators of fecal contamination of water, and amplification of lamB in particular permits detection of E. coli and enteric pathogens (Salmonella and Shigella spp.) with the necessary specificity and sensitivity for monitoring the bacteriological quality of water so as to ensure the safety of water supplies.     

Use of microcosms to determine persistence of Escherichia coli in recreational coastal water and sediment and validation with in situ measurements

AIMS: To determine the persistence of the faecal indicator organism Escherichia coli in recreational coastal water and sediment using laboratory-based microcosms and validation with in situ measurements. METHODS AND RESULTS: Intact sediment cores were taken from three distinct coastal sites. Overlying estuarine water was inoculated with known concentrations of E. coli and decay rates from both overlying water and sediment were determined following enumeration by the membrane filtration method at fixed time intervals over a 28-day period. It was demonstrated that E. coli may persist in coastal sediment for >28 days when incubated at 10 degrees C. Escherichia coli survival was found to have an inverse relationship with temperature in both water and sediment. In general the decay rate for E. coli was greater in water than in sediment. Small particle size and high organic carbon content were found to enhance E. coli survival in coastal sediments in the microcosms. CONCLUSIONS: Results of this microcosm study demonstrated the more prolonged survival of E. coli in coastal sediments compared with overlying water, which may imply an increased risk of exposure because of the possible resuspension of pathogenic micro-organisms during natural turbulence or human recreational activity. SIGNIFICANCE AND IMPACT OF THE STUDY: A more accurate estimate of exposure risk has been described which may subsequently be used in a quantitative microbial risk assessment for recreational coastal waters.     

Comparative study of commercial 4-methylumbelliferyl-beta-D-glucuronide preparations with the Standard Methods membrane filtration fecal coliform test for the detection of Escherichia coli in water samples.

The performance capabilities of two commercial 4-methylumbelliferyl-beta-D-glucuronide preparations were evaluated for the detection of Escherichia coli from water samples. Eighty-three water samples were collected from a treated water reservoir, and 32 samples were collected from untreated surface water. There was a statistically significant difference between the two commercial preparations compared with the Standard Methods membrane filtration fecal coliform (MFC) method for the detection of E. coli from treated water samples. However, there was no difference between the two methods and the MFC test for E. coli detection from the untreated surface water samples. The disagreement between the two commercial products and the MFC method was primarily due to the occurrence of false-negative results with the two commercial products. The data indicate that the occurrence of false-negative samples could be attributed to impaired substrate specificity and sensitivity of the two tests for E. coli detection. There was no apparent relationship between the occurrence of false-negative results and heterotrophic plate counts in samples.     

Escherichia coli: the best biological drinking water indicator for public health protection

Public health protection requires an indicator of fecal pollution. It is not necessary to analyse drinking water for all pathogens. Escherichia coli is found in all mammal faeces at concentrations of 10 log 9(-1), but it does not multiply appreciably in the environment. In the 1890s, it was chosen as the biological indicator of water treatment safety. Because of method deficiencies, E. coli surrogates such as the 'fecal coliform' and total coliforms tests were developed and became part of drinking water regulations. With the advent of the Defined Substrate Technology in the late 1980s, it became possible to analyse drinking water directly for E. coli (and, simultaneously, total coliforms) inexpensively and simply. Accordingly, E. coli was re-inserted in the drinking water regulations. E. coli survives in drinking water for between 4 and 12 weeks, depending on environmental conditions (temperature, microflora, etc.). Bacteria and viruses are approximately equally oxidant-sensitive, but parasites are less so. Under the conditions in distribution systems, E. coli will be much more long-lived. Therefore, under most circumstances it is possible to design a monitoring program that permits public health protection at a modest cost. Drinking water regulations currently require infrequent monitoring which may not adequately detect intermittent contamination events; however, it is cost-effective to markedly increase testing with E. coli to better protect the public's health. Comparison with other practical candidate fecal indicators shows that E. coli is far superior overall.     

Escherichia coli detection using mTEC agar and fluorescent antibody direct viable counting on coastal recreational water samples

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.     

Formation of nonculturable Escherichia coli in drinking water

AIMS: To examine whether incubation of Escherichia coli in nondisinfected drinking water result in development of cells that are not detectable using standard procedures but maintain a potential for metabolic activity and cell division. METHODS AND RESULTS: Survival and detectability of four different E. coli strains were studied using drinking water microcosms and samples from contaminated drinking water wells. Recovery of E. coli was compared using different cultivation-dependent methods, fluorescence in situ hybridization (FISH) using specific oligonucleotide probes, direct viable counts (DVC), and by enumeration of gfp-tagged E. coli (green fluorescent protein, GFP). Two levels of stress responses were observed after incubation of E. coli in nondisinfected drinking water: (i) the presence of cells that were not detected using standard cultivation methods but could be cultivated after gentle resuscitation on nonselective nutrient-rich media, and (ii) the presence of cells that responded to nutrient addition but could only be detected by cultivation-independent methods (DVC, FISH and GFP). Collectively, the experiments demonstrated that incubation for 20-60 days in nondisinfected drinking water resulted in detection of only 0.7-5% of the initial E. coli population using standard cultivation methods, whereas 1-20% could be resuscitated to a culturable state, and 17-49% could be clearly detected using cultivation-independent methods. CONCLUSIONS: Resuscitation of stressed E. coli on nonselective nutrient-rich media increased cell counts in drinking water using both traditional (CFU), and cultivation-independent methods (DVC, FISH and GFP). The cultivation-independent methods resulted in detection of 10-20 times more E. coli than the traditional methods. The results indicate that a subpopulation of substrate-responsive but apparent nonculturable E. coli may develop in drinking water during long-term starvation survival. SIGNIFICANCE AND IMPACT OF THE STUDY: The existence of substrate-responsive but nonculturable cells should be considered when evaluating the survival potential of E. coli in nondisinfected drinking water.     

Evaluation of colilert-marine water for detection of total coliforms and Escherichia coli in the marine environment.

A test that allows for early detection of fecally contaminated coastal water would enhance public health protection. Colilert-Marine Water (Colilert-MW; Environetics, Branford, Conn.) is a rapid 24-h test that has recently been developed to detect total coliforms and Escherichia coli in coastal water. We performed a premarketing evaluation of the Colilert-MW product, testing it in parallel with the multiple tube fermentation (MTF) method for 86 coastal water samples in southern California. Statistical analysis was performed by using paired t tests and linear regression. Bacterial isolates were evaluated by biochemical and genetic analysis. The results of this study showed a strong correlation between the traditional MTF and the Colilert-MW method for detection of total coliforms (r = 0.95) and E. coli (r = 0.89) in ocean water samples. Paired t-test results indicated that the Colilert-MW and MTF were equivalent in detecting E. coli and that the Colilert-MW may be more sensitive in the detection of total coliforms. We conclude that Colilert-MW would be a useful tool with which to monitor coastal beach water.