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Applied and Environmental Microbiology, July 2003, p. 4272-4273, Vol. 69, No. 7
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.7.4272-4273.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
Microbiology Department, Montana State University, Bozeman, Montana 59717
Received 3 June 2002/ Accepted 23 April 2003
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Epifluorescent microscopy can be used to rapidly estimate total cell numbers in water samples by using dyes, such as 4',6-diamidino-2-phenylindole dihydrochloride, acridine orange, and SYBR Green I (SG), that bind to nucleic acids (2, 3, 6, 10). For accurate estimates by epifluorescent microscopy there must be at least 105 cells evenly distributed on the filter, so when a sample contains small numbers of cells, extremely large quantities of liquid must be filtered (J. T. Lisle, A. Willse, B. H. Pyle, M. Hamilton, and G. A. McFeters, Abstr. 99th Gen. Meet. Am. Soc. Microbiol. 1999, abstr. Q-203, p. 572, 1999).
Flow cytometry can be used to count SG-stained and other fluorescently stained bacterial cells in water (1, 7, 8, 12). Although cells can be enumerated at a lower concentration than that required by epifluorescent microscopy, cell numbers must still be greater than 100 bacteria per ml to obtain reliable counts in a short time. Additionally, the presence of autofluorescent particles and debris stained by nonspecific binding of the fluorescent dye will cause erroneous results, limiting the use of flow cytometry in evaluating environmental samples (5, 12).
The ScanRDI (Chemunex, Paris, France) is a solid-phase laser scanner that is able to scan the entire surface of a 25-mm-diameter filter in 3 min by using a 488-nm laser (4, 9, 11, 13). Detectors record emitted fluorescence, and computer software screens all the fluorescent events by using several discriminant parameters, displays the number of events determined to be cells, and maps the location of each particle. The operator then transfers the filter to an epifluorescence microscope, and the ScanRDI system directs the microscope stage to each fluorescent particle, allowing the operator to confirm the discrimination of bacterial cells and detritus. This system allows the detection and verification of a single bacterial cell on a filter.
ChemChrome V6 (AES-Chemunex, Inc., Princeton, N.J.), a proprietary reagent developed for use with the ScanRDI, is a reducible fluorescein-labeled substrate which, when degraded by esterase activity, releases free fluorescein inside the cell. Cells that are detected by this green fluorescence are reported in the viable cell count due to esterase activity (13).
The fluorescent characteristics of stains such as 4',6-diamidino-2-phenylindole dihydrochloride and acridine orange are incompatible with the ScanRDI system. It was determined that cells stained with SG are detectable by the ScanRDI by using modified discriminant settings. SG and ChemChrome can be used in parallel to enumerate total and viable bacteria, respectively. Viable counts enumerated by using ChemChrome and total counts determined by SG staining were compared to R2A agar plate counts.
Three different water sources were used to determine the effectiveness of SG staining for use with the ScanRDI system: ultrapure laboratory water (Milli-Q; Millipore), tap water, and diluted stream water containing a natural multispecies community. The efficacy of SG staining on fixed versus unfixed samples was determined. Milli-Q water that was filtered through a 0.2-µm-pore-sized filter and then autoclaved was used as a negative control.
Plate counts on water samples containing less than 30 CFU/ml were filtered in triplicate through sterile filters (0.2 µm pore size, 47 mm diameter; catalog no. GSWP 047 S0; Millipore) in volumes sufficient to give 20 to 200 CFU/filter. The filters were placed on R2A agar containing 0.002% triphenyl tetrazolium chloride. Water samples with more than 30 CFU/ml were plated directly on R2A medium. Colonies were enumerated after 14 days of incubation at ambient room temperature (ca. 22°C).
Detection of bacteria with esterase activity was performed on appropriate aliquots of the water according to the manufacturer's protocol by using ChemChrome V6. Cells were enumerated on a ScanRDI by using the discriminant settings supplied by AES-Chemunex.
For SG staining the water sample was filtered through a black polycarbonate membrane, and then an overlay of dye was applied to the filter. After incubation the stain was removed by vacuum and the membranes were dried and stored in the dark at 4°C prior to enumeration. Using results of preliminary experiments, all SG staining was done in the dark at a final concentration of 100x in water for 5 min at room temperature.
As shown in Fig. 1, results from the analysis of Milli-Q water were similar to plate count results for both esterase activity and total numbers. Reflecting the effects of chlorination, esterase counts for tap water were statistically equivalent to plate counts, and total cell numbers determined by SG staining without formalin fixation were more than a log higher. Formalin fixation reduced the number of stained cells detected in tap water, but the numbers were still nearly 35 times the numbers determined by plate counts. The numbers of bacterial cells from surface water samples were 1.59 times the plate count when determined by esterase activity and were 4.77 times the plate count when determined by total cell staining with SG. Little difference was observed in surface water results due to formalin fixation.
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FIG. 1. Comparison of enumeration of bacterial cells from surface water, tap water, and Milli-Q water by the ScanRDI by using SG and ChemChrome staining to enumeration of bacterial cells by plate counts on R2A agar (n = 2 to 3). Symbols: black circles, esterase surface water; gray circles, SYBR Green surface water; open circles, SYBR Green surface water after formalin fixation; black squares, esterase tap water; gray squares, SYBR Green tap water; open squares, SYBR Green tap water after formalin fixation; black triangles, esterase Milli-Q; gray triangles, SYBR Green Milli-Q; open triangles, SYBR Green Milli-Q after formalin fixation. The diagonal line is the line of equality.
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Funding from NASA (NAG 9-1082 and NCC 2-1143) is gratefully acknowledged.
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