R factors in coliform-fecal coliform sewage flora of the prairies and Northwest Territories of Canada.

Coliform and fecal coliform populations found in the raw sewages and final sewage effluents of the prairie provinces and the Northwest Territories were examined for antibiotic resistance and the possession of R factors. It was determined that 8.91% of the total coliform and 10.80% of the fecal coliform populations carried R factors. The following numbers of combinations of R determinants were found: 39 in the Escherichia coli population, 6 in the Citrobacter population, 20 in the Enterobacter populations, 10 in the Klebsiella populations, and 11 in the Aeromonas populations. The maximum number of R determinants transferable simultaneously was seven; organisms with R factors containing determinants for chloramphenicol usually contained determinants for ampicillin. Of the coliform and fecal coliform populations, 2 to 4% were resistant to chloramphenicol in some provinces, and from 17 to 30% of the populations were resistant to three or more antibiotics. It was calculated that coliforms containing R factors in the raw sewage reached population levels of 1.5 X 10(7)/100 ml, and fecal coliforms containing R factors reached population levels of 8.6 X 10(5) ml. Final effluent discharges to the receiving environment contained R factor-containing coliform and fecal coliform populations of 3.1 X 10(4)/100 ml and 5.8 X 10(2)/100 ml, respectively. The incidence of bacteria containing R factors in sewage appears to be increasing with time, and their removal from sewage before discharge to the receiving environment is desirable. Consideration of data on bacteria with R factors should be made in future water quality deliberations and in discharge regulations.     

A note on antibiotic resistance in the bacterial flora of raw sewage and sewage-polluted River Tigris in Mosul, Iraq

Polluted water samples collected from the River Tigris in the vicinity of a raw sewage outfall were examined for the incidence of antibiotic resistance among coliform bacteria on three occasions during 1983. Eighty percent or more of the coliform bacteria were resistant to one or more antibiotics. At the same time, raw sewage samples were examined for the incidence of antibiotic-resistant bacteria, and Escherichia coli, Pseudomonas spp. and Staphylococcus spp. were selected for sensitivity testing. Collectively, more than 90% of the 480 strains of the three organisms were resistant to one or more antibiotics. The minimal inhibitory concentration (MIC) of ampicillin for twenty-nine strains including coliforms, E. coli, Klebsiella sp., Serratia sp., Ps. aeruginosa, Pseudomonas sp., Micrococcus sp., Staph. aureus, Streptococcus faecalis and Bacillus sp. from raw sewage and polluted River Tigris water was determined and that for Ps. aeruginosa was 250 micrograms/ml. The high incidence of antibiotic-resistant bacteria in natural waters could be related to the widespread use of antibiotics in this locality.     

Cadmium tolerance and antibiotic resistance in Escherichia coli isolated from waste stabilization ponds

The incidence pattern of cadmium tolerance and antibiotics resistance by Escherichia coli was examined periodically from the samples of water, sludge and intestine of fish raised in waste stabilization ponds in a sewage treatment plant. Samples of water and sludge were collected from all the selected ponds and were monitored for total counts of fecal coliform (FC), total coliform (TC) and the population of Escherichia coli, which was also obtained from the intestine of fishes. Total counts of both FC and TC as well as counts of E. coli were markedly reduced from the facultative pond to the last maturation pond. Tolerance limit to cadmium by E. coli tended to decline as the distance of the sewage effluent from the source increased; the effective lethal concentration of cadmium ranged from 0.1 mM in split chamber to 0.05 mM in first maturation pond. E. coli isolated from water, sludge and fish gut were sensitive to seven out of ten antibiotics tested. It appears that holistic functions mediated through the mutualistic growth of micro algae and heterotrophic bacteria in the waste stabilization ponds were responsible for the promotion of water quality and significant reduction of coliform along the sewage effluent gradient.     

Incidence of Infectious Drug Resistance Among Fecal Coliforms Isolated from Raw Sewage

Raw sewage was examined for the incidence of antibiotic-resistant coliforms present among both total and fecal coliforms. In both groups, it was found that approximately 3% of the coliform bacteria were resistant to two or more antibiotics. Of these organisms, 48% were capable of transferring all or part of their antibiotic resistance to an antibiotic-sensitive, F⁻, derivative of Escherichia coli K-12. Among the R factors identified, those conferring resistance to streptomycin-tetracycline, ampicillin-streptomycin-tetracycline, and ampicillin or ampicillin-streptomycin accounted for 23, 20, and 15%, respectively, of the total R factors detected. The data indicate a significant level of infectious drug resistance among the fecal coliforms of the urban population. The data indicate further that because of the high incidence of coliform bacteria found to be doubly resistant to streptomycin and tetracyline, the inclusion of these antibiotics in selective media used for routine total or fecal coliform counts may serve to identify domestic sources of pollution.     

四川地区孕妇产后子宫内膜炎主要致病菌的检测及其耐药性分析

大肠杆菌(Escherichia coli)、化脓隐秘杆菌(Trueperella pyogenes,Arcanobacterium pyogenes)和坏死梭杆菌(Fusobacterium necrophorum)是与子宫内膜病变相关的主要病原体。本研究使用聚合酶链式反应(PCR)直接鉴定四川地区139例孕妇宫颈分泌物中的病原体,而不进行细菌培养。此外,对上述3种病原体的耐药性进行了考察。结果显示,第1次生产后检查发现子宫内膜炎的发生率(35.25%)高于第2次生产后检查(15.53%)。在6个样品中检测到大肠杆菌,在11个样品中检测到化脓隐秘杆菌,并在10个样品中检测到坏死梭杆菌。在第1次检查中,化脓隐秘杆菌和坏死梭杆菌的子宫污染感染高于第2次检查。药敏实验结果显示,大肠杆菌、化脓隐秘杆菌和坏死梭杆菌分别对9种、6种和7种药物产生耐药性。总之,本研究建立了用于诊断孕妇产后子宫内膜炎的3种主要病原体的标准PCR,该方法更简单、成本低和快捷,且对主要细菌检测具有较高的灵敏度。此外,大肠杆菌的耐药性高于另外2个菌种。     

Preliminary study of microbiological parameters in eight inland recreational waters

A pilot survey of the counts of total coliform bacteria, thermotolerant coliform bacteria, Escherichia coli and faecal streptococci was carried out at eight inland recreational waters at weekly intervals during July 1991. The aims were to assess the feasibility of determining candidate indicators of recreational water quality and to assess the possible scale of variability of these parameters. The numbers of total coliforms were difficult to determine reliably because of interference from the background bacterial flora. There was a strong correlation between thermotolerant coliforms and E. coli and faecal streptococci. The average counts of the indicator organisms varied between and within the eight recreational waters by up to 10000-fold. The greatest variation was between the eight recreational waters. At any one water, the greatest source of variation was time but there was substantial variation between sample points at one time. Counts in samples collected 1 m apart exhibited greater than random variation. Counts from surface samples tended to be higher than those at 30 cm or 100 cm depth. The proportion of thermotolerant coliforms confirmed to be E. coli varied from water to water between 60% and 96%.     

Recognition of individual genes in diverse microorganisms by cycling primed in situ amplification

Cycling primed in situ amplification-fluorescent in situ hybridization (CPRINS-FISH) was developed to recognize individual genes in a single bacterial cell. In CPRINS, the amplicon was long single-stranded DNA and thus retained within the permeabilized microbial cells. FISH with a multiply labeled fluorescent probe set enabled significant reduction in nonspecific background while maintaining high fluorescence signals of target bacteria. The ampicillin resistance gene in Escherichia coli, chloramphenicol acetyltransferase gene in different gram-negative strains, and RNA polymerase sigma factor (rpoD) gene in Aeromonas spp. could be detected under identical permeabilization conditions. After concentration of environmental freshwater samples onto polycarbonate filters and subsequent coating of filters in gelatin, no decrease in bacterial cell numbers was observed with extensive permeabilization. The detection rates of bacterioplankton in river and pond water samples by CPRINS-FISH with a universal 16S rRNA gene primer and probe set ranged from 65 to 76% of total cell counts (mean, 71%). The concentrations of cells detected by CPRINS-FISH targeting of the rpoD genes of Aeromonas sobria and A. hydrophila in the water samples varied between 2.1 x 10(3) and 9.0 x 10(3) cells ml(-1) and between undetectable and 5.1 x 10(2) cells ml(-1), respectively. These results demonstrate that CPRINS-FISH provides a high sensitivity for microscopic detection of bacteria carrying a specific gene in natural aquatic samples.     

2009年雅安市食源性病原菌监测分析

目的了解雅安市食品中污染的食源性疾病中的重要致病菌,积累监测数据。方法按照《全国食源性致病菌监测2009年度工作手册》,检测10大类食品中的大肠菌群、沙门菌、金黄色葡萄球菌、单核增生李斯特菌、大肠菌群O157和副溶血性弧菌。结果果汁、凉拌蔬菜和蔬菜沙拉大肠菌群的检出率为60%、100%和100%;生畜肉、生食水产品和皮蛋中沙门菌的检出率为10%、20%和3.3%;未检出金黄色葡萄球菌、单核增生李斯特菌、大肠埃希菌O157和副溶血性弧菌。结论通过对食源性疾病的基础监测,加强食品安全,为雅安市防治食源性疾病提供科学依据。     

A national study on the residential impact of biological aerosols from the land application of biosolids

AIMS: The purpose of this study was to evaluate the community risk of infection from bioaerosols to residents living near biosolids land application sites. METHODS AND RESULTS: Approximately 350 aerosol samples from 10 sites located throughout the USA were collected via the use of six SKC Biosamplers. Downwind aerosol samples from biosolids loading, unloading, land application and background operations were collected from all sites. All samples were analysed for the presence of HPC bacteria, total coliform bacteria, Escherichia coli, Clostridium perfringens, coliphage, enteroviruses, hepatitis A virus and norovirus. Total coliforms, E. coli, C. perfringens and coliphage were not detected with great frequency from any sites, however, biosolids loading operations resulted in the largest concentrations of these aerosolized microbial indicators. Microbial risk analyses were conducted on loading and land application operations and their subsequent residential exposures determined. CONCLUSIONS: The greatest annual risks of infection occurred during loading operations, and resulted in a 4 x 10(-4) chance of infection from inhalation of coxsackievirus A21. Land application of biosolids resulted in risks that were <2 x 10(-4) from inhalation of coxsackievirus A21. Overall bioaerosol exposure from biosolids operations poses little community risk based on this study. SIGNIFICANCE AND IMPACT OF THE STUDY: This study evaluated the overall incidence of aerosolized micro-organisms from the land application of biosolids and subsequently determined that microbial risks of infection were low for residents close to biosolids application sites.     

Differential susceptibility of aeromonads and coliforms to cefsulodin.

Cefsulodin was evaluated as a potential selective agent for aeromonads. Resistance of Aeromonas and coliform isolates was determined by using a standard disk diffusion technique. A total of 119 Aeromonas and 78 coliform strains were isolated. For 102 of 130 [corrected] Aeromonas isolates (environmental and reference strains), the MIC of cefsulodin was < 8 micrograms/ml. Results of MIC tests by the agar dilution method showed that a concentration of cefsulodin of 10 micrograms/ml or less inhibited the growth of 96% of isolates. In comparison, for 81 of 94 coliform isolates (environmental and reference strains), the MIC of cefsulodin was > 32 micrograms/ml. Because cefsulodin suppresses growth of Aeromonas and other oxidase-positive organisms, total coliform (TC) and Escherichia coli counts on Chromocult Coliform agar (CC agar) without cefsulodin and on CC agar with 10 mg of cefsulodin per liter (CC-CFS) were compared. Variance analysis of data from 14 sewage-polluted irrigation water specimens did not demonstrate any statistically significant difference in the enumeration of E. coli with CC and CC-CFS media. On average, the CC agar recovered 2.46 times as many TCs as CC-CFS. However, Aeromonas colonies made up an average of 58.6% of the TC counts on CC agar. Because no Aeromonas spp. were recovered on CC-CFS, background interference was eliminated and the counts that were obtained reflected more accurately the number of TCs. Results of this study suggest that cefsulodin may be a useful selective agent against Aeromonas spp. which should be included in coliform chromogenic media when high levels of accompanying flora are expected.     

重庆地区儿童2000年至2004年首位革兰阴性细菌和阳性细菌的耐药性监测

目的了解重庆地区儿童感染的分离至临床标本的首位革兰阴性细菌和阳性细菌对常用抗生素的耐药趋势,指导临床合理使用抗生素。方法常规方法分离、培养细菌,应用美国德灵公司WalkAway-40细菌鉴定仪对2000年至2004年我院细菌室分离至临床标本的首位革兰阴性细菌和阳性细菌共2854株进行细菌鉴定及药敏试验。结果2000年至2004年检出的首位革兰阴性细菌和阳性细菌分别为大肠埃希菌和金黄色葡萄球菌。2000年至2004年前5位革兰阴性菌5777株,革兰阳性菌1565株,其中大肠埃希菌2090株,金黄色葡萄球菌764株,分别占36.2%和48.8%;5年间大肠埃希菌对氨苄西林、头孢吡肟、头孢西丁、庆大霉素、亚胺培南、环丙沙星、头孢噻肟、头孢他啶的总耐药率分别为80.9%、37.5%、15.4%、54.0%、0.8%、34.0%、46.6%、46.2%;金黄色葡萄球菌对青霉素、红霉素、复方新诺明、万古霉素、阿莫西林/克拉维酸的总耐药率分别为95.6%、63.4%、5.8%、0%、11.0%。结论通过细菌耐药监测发现：大肠埃希菌对常用抗生素的总耐药率变化不大,金黄色葡萄球菌对常用抗生素的总耐药率有下降趋势,应引起临床医生重视。     

Fecal pollution in water from storm sewers and adjacent seashores in Natal, Rio Grande do Norte, Brazil.

A study on the distribution patterns of enteropathogenic bacteria polluting the shoreline in Natal, Rio Grande do Norte, Brazil, was carried out based on 72 samples obtained from three storm sewers and adjoining beach locations, Praia do Meio (PM), Areia Preta (AP) and Ponta Negra (PN). From each location, 12 water samples were taken and analyzed for fecal coliforms (FC) and Escherichia coli. In AP, two (16.7%) of the seawater samples and five (41.7%) of the storm sewer samples yielded values above 1.1 x 107 FC/100 ml, whereas only one (8.3%) of the samples from PM reached this level. There was no correlation (p > 0.05) between rainfall indices and FC values. A total of 64 E. coli isolates were obtained: 37 from the storm sewer samples and 27 from the seawater samples. Of these isolates, four (O143, two O112ac, and O124) were enteroinvasive and two (O111 and O125) were enteropathogenic. Resistance to antibiotics and to heavy metals was also analyzed. Almost 36% of the E. coli strains isolated were resistant to more than one antibiotic. All strains were resistant to zinc and copper at the highest concentration tested (250 microg/ml), and several (23.4%) were resistant to mercury at 50 microg/ml. Our results agreed with previous reports that antibiotic resistance is commonly associated with heavy-metal resistance in pathogens.     

Drug Resistance in Strains of Escherichia Coli Isolated from the Intestinal Tract of Pigs in Norway

Faecal samples from 95 healthy pigs and samples of jejunal content from 85 piglets suffering from colienterotoxaemia were tested for the presence of drug resistant E. coli strains. Practically all pigs in both groups harboured E. coli strains resistant to one or more of the 6 antibiotics/chemotherapeutic agents tested (Oxytetracycline, streptomycin, sulphaisodimidin, neomycin, ampicillin, chloramphenicol). Almost 100% of healthy and approx. 90% of diseased pigs harboured strains resistant to Oxytetracycline, streptomycin and sulphaisodimidin. Pigs with strains resistant to neomycin, ampicillin and chloramphenicol were less frequently found. The predominant coliform flora consisted of E. coli strains” resistant to Oxytetracycline, streptomycin and sulphaisodimidin in 71% to 81% of diseased pigs and in 47% to 69% of the healthy pigs. In diseased pigs ¾ of the animals had a coliform flora dominated by neomycinresistant E. coli strains. Of the 721 resistant E. coli strains isolated from healthy pigs, 11% were single resistant while the corresponding figure for the 518 resistant strains isolated from diseased pigs was 6%. Thus 89% and 94% of strains showed simultaneous resistance to 2 or more antibiotics. E. coli strains resistant to 3 or more drugs were found in approx. 60% and 70% of the isolates from healthy and diseased animals, respectively. Oxytetracycline/streptomycin/sulphaisodimidin resistance was most commonly found, approx. 22% and 38% of the strains from healthy and diseased pigs, respectively, showing this resistance pattern. Transmission of drug resistance which was examined in E. coli strains originating from the diseased pigs was demonstrated in approx. 76% of the isolates. The incidence of drug resistance transfer in single, double, triple and quadruple resistant strains was 11%, 68%, 97% and 98%, respectively.     

Apparent bias in river water inoculum following centrifugation

We collected four measures of viable bacterial concentration (heterotrophic plate count, total coliform, fecal coliform, and Escherichia coli) and three measures of well color development in Biolog GN2 microtiter plates from water samples that were collected on two or three separate occasions from a fixed site on 19 different streams throughout Oregon. Our goal was to determine whether concentrating the water sample with centrifugation prior to analysis would change the in situ composition of the culturable bacterial assemblage. Each sample was split and one subsample was centrifuged while the other subsample served as a control. A shift in the proportion of each group of culturable bacteria toward more fecal coliform bacteria was observed following centrifugation. In samples with the lowest initial heterotrophic bacterial densities (under 50CFU/100ml), the observed concentration following centrifugation was much lower than expected. However, samples that had high initial heterotrophic bacterial densities (over 1000CFU/100ml) had concentrations at or above expected values following centrifugation, but were biased toward a higher proportion of coliform bacteria. Bacteria in centrifuged subsamples utilized more sole-carbon substrates on Biolog GN2 microtiter plates and showed a shorter lag time prior to tetrazolium color development than their uncentrifuged counterparts. Future research that focuses on characterizing and accounting for the bias associated with centrifugation of water samples held for less than 24h is recommended.     

Cultural and environmental factors affecting the longevity of Escherichia coli in Histosols.

The survival of Escherichia coli in organic soils (Histosols) was examined. The death rate of this organism in Pahokee muck was less than that observed in Pompano fine sand. The number of viable E. coli cells found in the muck was approximately threefold greater than that found in the sand following 8 days of incubation. The initial population of the coliform affected the death rate. The rate of loss of viability varied 100-fold when the population size decreased from 2.5 x 10(7) to 3.4 x 10(4). Other factors affecting the viability of E. coli in muck were aerobic versus anaerobic growth of the organism and moist versus flooded conditions in the soil. The greatest survival of the coliform was noted with anaerobically grown cells amended to flooded soil. That the observed decrease in E. coli viability in soil was the result of biotic factors was demonstrated with amendment of sterile soil with E. coli. When 1.1 x 10(5) bacteria per g of soil were added to sterile muck, a population of 3.0 x 10(7) organisms per g of soil developed over a 10-day period. The role of the protozoa in eradication of the coliform from the muck was indicated by a sixfold increase in the protozoan population in natural soil amended with E. coli. Higher organic matter content in a Histosol compared with a mineral soil resulted in an increased survival of the fecal coliforms. Biotic factors are instrumental in the decline in coliform populations, but the potential for growth of the coliform in the organic soil could extend the survival of the organism.     

Full-scale studies of factors related to coliform regrowth in drinking water.

An 18-month survey of 31 water systems in North America was conducted to determine the factors that contribute to the occurrence of coliform bacteria in drinking water. The survey included analysis of assimilable organic carbon (AOC), coliforms, disinfectant residuals, and operational parameters. Coliform bacteria were detected in 27.8% of the 2-week sampling periods and were associated with the following factors: filtration, temperature, disinfectant type and disinfectant level, AOC level, corrosion control, and operational characteristics. Four systems in the study that used unfiltered surface water accounted for 26.6% of the total number of bacterial samples collected but 64.3% (1,013 of 1,576) of the positive coliform samples. The occurrence of coliform bacteria was significantly higher when water temperatures were > 15 degrees C. For filtered systems that used free chlorine, 0.97% of 33,196 samples contained coliform bacteria, while 0.51% of 35,159 samples from chloraminated systems contained coliform bacteria. The average density of coliform bacteria was 35 times higher in free-chlorinated systems than in chloraminated water (0.60 CFU/100 ml for free-chlorinated water compared with 0.017 CFU/100 ml for chloraminated water). Systems that maintained dead-end free chlorine levels of < 0.2 mg/liter or monochloramine levels of < 0.5 mg/liter had substantially more coliform occurrences than systems that maintained higher disinfectant residuals. Free-chlorinated systems with AOC levels greater than 100 micrograms/liter had 82% more coliform-positive samples and 19 times higher coliform levels than free-chlorinated systems with average AOC levels less than 99 micrograms/liter. Systems that maintained a phosphate-based corrosion inhibitor and limited the amount of unlined cast iron pipe had fewer coliform bacteria. Several operational characteristics of the treatment process or the distribution system were also associated with increased rates of coliform occurrence. The study concludes that the occurrence of coliform bacteria within a distribution system is dependent upon a complex interaction of chemical, physical, operational, and engineering parameters. No one factor could account for all of the coliform occurrences, and one must consider all of the parameters described above in devising a solution to the regrowth problem.     

Characterization and quantification of bacterial pathogens and indicator organisms inhousehold kitchens with and without the use of a disinfectant cleaner

This two year study evaluated the prevalence of indicator bacteria and specific pathogens in10 'normal' kitchens in the United States. In Phase I, none of the kitchens wascleaned with an antimicrobial cleaner or disinfectant. Eight locations within the kitchens weremonitored for: total heterotrophs, staphylococci, Pseudomonas , total coliforms andfaecal coliforms. Almost all locations at all households exhibited contamination, with the sink andsponge samples exhibiting large bacterial concentrations. The faecal coliform concentrations insink and sponge samples were very high, with 63 and 67% of all samples being positive,respectively. Escherichia coli was detected in 16·7% of all sink surfaces and33·3% of all sponges. Salmonella was detected once and Campylobacter , on two occasions. In a second phase, households were provided with an antimicrobialdisinfectant cleaner which families were encouraged to use but not forced to do so; in some cases,the product was used infrequently or not at all. This regimen did not demonstrate any consistentreduction in the incidence of bacterial contamination. By contrast, in the final phase of the studywhere disinfectant use was targeted for surfaces soon after contamination with foods or hands,the incidence of contamination decreased dramatically. These data show that normal kitchens caneasily be contaminated with a variety of bacterial contaminants including faecal coliforms, E.coli, Salmonella and Campylobacter . Irregular use, or not using antimicrobialagents, is unlikely to reduce the risk of these infectious agents. By contrast, targeted use is likelyto reduce the incidence of bacterial contaminants.     

Microflora of gastric juice and its sensitivity to antibiotics in post-gastrectomy gastritis

Fifty four patients with postresection gastritis and 13 healthy adults were examined. 141 microbial cultures belonging to 33 species were isolated from the gastric juice of the patients. In the healthy persons 27 cultures belonging to 7 species were isolated from the gastric juice. In the gastric juice of the patients there predominated enteric bacteria and enterococci (64.8 +/- 6.5 and 57.4 +/- 6.7 per cent respectively). Among the enteric bacteria Escherichia coli and Proteus spp. were the most frequent. Contamination of the gastric juice by such microbes amounted to 10(5)-10(9) microbial bodies per 1 ml. The isolates were mainly sensitive to gentamicin (84.8 +/- 2.9 per cent).     

Occurrence of airborne enteric bacteria in Mexico city

Summary An investigation of microbial air quality in the area of the National Autonomous University of Mexico, located in the southern part of Mexico City, was conducted for one year. Ambient outdoor concentrations and size distribution of airborne bacteria were measured, 130 samples were taken at noon, using an Andersen 6 stage sampler, located 2 m above ground level. Concentration ranges and colony-forming units per cubic meter of air (CFU m^–3) found, were as follows:14 to 12999 for total bacteria, No growth (NG) to 55 for coliform bacteria, NG to 11 for fecal coliform and NG to 10 for fecal Streptococci.Bacteria associated with the potentially respirable fraction (0.65 to 4.7 µm) averaged 37% and 9% for total bacteria and coliform bacteria respectively. In 23% of the samples, coliform bacteria were recovered, with higher incidences during dry season. The most common of these were:Escherichia coli (15%), followed bySerratia (13%) andEnterobacter (10%),The total bacteria correlated significatively (p<0.05) with the following parameters: particulate matter smaller than 10 µm (PM₁₀) (r=0.40), total suspended particulates (TSP) (r=0.26), daily variation of temperature (r=0.18), and vapor pressure (r=–0.16). These relationships indicate that fecal soil pollution could affect air quality with potential health risks.     

Marine bacteria cause false-positive results in the Colilert-18 rapid identification test for Escherichia coli in Florida waters

The Colilert-18 system for enumeration of total coliforms and Escherichia coli is approved by the U.S. Environmental Protection Agency for use in drinking water analysis and is also used by various agencies and research studies for enumeration of indicator organisms in fresh and saline waters. During monitoring of Pinellas County, Fla., marine waters, estimates of E. coli numbers (by Colilert-18) frequently exceeded fecal coliform counts (by membrane filtration) by 1 to 3 orders of magnitude. Samples from freshwater sites did not display similar discrepancies. Fecal coliforms, including E. coli, could be cultured from 100% of yellow fluorescent wells (denoting E. coli-positive results) inoculated with freshwater samples but could be cultured from only 17.1% of the "positive" wells inoculated with marine samples. Ortho-nitrophenyl-beta-D-galactopyranoside (ONPG)-positive or 4-methylumbelliferyl-beta-D-glucuronide (MUG)-positive noncoliform bacteria were readily cultured from Colilert-18 test wells inoculated with marine samples. Filtered cell-free seawater did not cause false positives. Coculture preparations of as few as 5 CFU of Vibrio cholerae (ONPG positive) and Providencia sp. (MUG positive) ml(-1) inoculated into Colilert-18 caused false-positive E. coli results. Salinity conditions influenced coculture results, as the concentration of coculture inoculum required to cause false positives in most wells increased from about 5 CFU ml(-1) in seawater diluted 1:10 with freshwater to approximately equal to 5,000 CFU ml(-1) in seawater diluted 1:20 with freshwater. Estimated E. coli numbers in various marine water samples processed at the 1:10 dilution ranged from 10 to 7,270 CFU.100 ml(-1), while E. coli numbers in the same samples processed at the 1:20 dilution did not exceed 40 CFU.100 ml(-1). The lower estimates of E. coli numbers corresponded well with fecal coliform counts by membrane filtration. This study indicates that assessment of E. coli in subtropical marine waters by Colilert-18 is not accurate when the recommended 1:10 sample dilution is used. The results suggest that greater dilution may diminish the false-positive problem, but further study of this possibility is recommended.