EPA-MICRO: 600-R-00-013:  Membrane filtration plating of coliform bacteria on MI agar

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Membrane filter method for the simultaneous detection of total coliforms and Escherichia coli in drinking water.
Current Revision
2000
Media
WATER
Instrumentation
Membrane Filtration
Method Subcategory
Microbiological
Method Source
  EPA-MICRO
Citation
USEPA, 2000. Membrane filter method for the simultaneous detection of total coliforms and Escherichia coli in drinking water. EPA-600-R-00-013. USEPA: Cincinnati, OH. 21 pp.
Brief Method Summary
Allows analysis of both total coliforms and E. coli. Filter sample through a membrane filter (Standard Methods 20th ed. Section 9222B), place membrane on MI agar, containing the enzyme substrates MUGal (4-methylumbelliferyl-D-galactopyranoside) for total coliforms and IBDG (indoxyl-D-glucuronide) for E. coli. Incubate at 35oC for 22-24 h. E. coli are counted as blue colonies under ambient light. Total coliforms are counted as colonies that fluoresce under a long-wave ultraviolet light source: blue-white fluorescence is positive for total coliforms other than E. coli; blue-green fluorescence is positive for E. coli; non-fluorescent blue colonies are also counted (breakdown of IBDG assumed to mask fluorescence). Requires an extensive dilution series for ambient waters. Requirements: Ingredients for MI agar; buffer for rinsing and dilutions. Culture dishes (50x10mm); 0.45 micron membrane filters; sterile pipets; manifold and sterile filter funnel; forceps, alcohol. Refrigeration; autoclave; incubator at 35+/-0.5oC with 90% humidity. Stereoscopic microscope (10-15X); a long-wave ultraviolet light source (366 nm) to count fluorescent colonies. Cost of analysis (USEPA Fed. Reg. Aug 2001): E coli $22 ($10 to $35) total coliforms $22 ($15 to $48)
Scope and Application
Ambient, compliance monitoring: non-compliance: all water - freshwater (ground and surface waters, runoff), recreational water, marine waters, municipal wastewater, swimming pool, drinking water, bottled water, soil, sludge. EPA Fed Reg (Aug 2001) for E coli, ambient only: fresh, marine, or estuarine surface waters; applicability must be demonstrated for other matrices. USEPA. 1999 (December 1). National primary and secondary drinking water regulations: analytical methods for chemical and microbiological contaminants and revisions to laboratory certification requirements; final rule. Fed. Reg. 64(230)67449-67467. Safe Drinking Water Act: a) Total Coliform Rule: presence/absence of total coliforms and E coli b) Surface Water Treatment Rule: enumeration of total coliforms 40 CFR 141, 143. USEPA. 2001 (August 30). Guidelines establishing test procedures for the analysis of pollutants; Analytical methods for biological pollutants in ambient water; proposed rule. Fed. Reg. 66(169)45811-45829. Clean Water Act section 401. 40 CFR 136.1(c). (state certification, licenses) for compliance monitoring in programs 303(c), 304(a), and 501(a). 136.3 Identification of test procedures.
Applicable Concentration Range
20 - 80 CFU/100 mL is considered ideal for enumeration, and typical of drinking water samples without dilution. Maximum: 200 CFU/100 mL; dilution is required for samples that exceed this level
Interferences
Colloidal or suspended particulate material that can clog the membrane filter or cause spreading of colonies and make enumeration difficult. Colonies to be excluded from counting: 1) non-E coli: tiny, flat or peaked pinpoint colonies (< 0.5 mm dia) that are blue in ambient light, in samples with < 200 CFU per filter; 2) non-coliforms: non-blue colonies in ambient light that fluoresce bright green. Sources of interference in MF methods (USEPA Fed Reg Aug. 2001): high turbidity, toxic compounds, or large numbers of non-coliform (background) bacteria, and organisms damaged by chlorine or toxic compounds.
Quality Control Requirements
(Standard Methods 20th ed. 9020 B.8 and 9; Myers and Sylvester, 1997) 1. Control cultures--a positive (E. coli) for total coliforms and E. coli and negative for total coliforms (Staphylococcus) or E. coli (Enterobacter) may be used to test the medium. 2. Repeat counts--monthly replicate counts for the same analyst should agree within 5% and between analysts within 10%. 3. Duplicate analyses--perform duplicate analyses on 10% of samples. 4. Sterility check--a 50 to 100 mL aliquot of buffered dilution water is plated before each sample to assess contamination of equipment or media. 5. Verification--validate analysis of a portion of these differentiated colonies according to Brenner and others (1993).
Sample Handling
Sample preservation: chilled, 1 to 4oC; 1 mL of 10% Na2S2O3 per liter drinking water or chlorinated effluent. Techniques for collection: Myers, D.N.; Sylvester, F.D. 1997. National field manual for the collection of water-quality data - biological indicators. USGS Techniques of Water Resources Investigations. Book 9, Chapter A7. 38 pp. Standard Methods for the Examination of Water and Wastewater, 20th Edition. L. Clesceri, A. Greenberg, and A. Eaton (editors). Sections 9020B8 and B9, 9060A, 9222B. APHA: Washington, DC. 1998.
Sample processing time 1 hour. Requires an extensive dilution series for ambient waters. To minimize interferences causing underestimation of organism density in MF methods (USEPA Fed Reg Aug. 2001): replicates of smaller sample dilutions/volumes may be filtered and the results combined.
Maximum Holding Time
Analyze samples as soon as possible after collection. Drinking water samples can be analyzed within 30 h of collection. Natural water samples should not be held longer than 6 h, and the analyses should be complete within 8 h of sample collection.
Relative Cost
Less than $50
Sample Preparation Methods