ASTM D5259-24
(Test Method)Standard Test Method for Isolation and Enumeration of Enterococci from Water by the Membrane Filter Procedure
Standard Test Method for Isolation and Enumeration of Enterococci from Water by the Membrane Filter Procedure
SIGNIFICANCE AND USE
5.1 The enterococci are indicators of the bacteriological quality for potable water, shellfish growing waters, ambient, and recreational waters. A direct relationship between swimming, associated gastroenteritis, and enterococci has been established through epidemiological studies and marine and fresh water bathing beaches. These studies have led to the development of criteria that can be used to establish bathing water standards based on established health-water quality relationships.
5.2 Since small or large volumes of water or dilutions thereof, can be analyzed by the membrane filter technique, a wide range of levels of enterococci in water can be enumerated and detected.
SCOPE
1.1 This test method covers a membrane filter (MF) procedure for the detection and enumeration of the enterococci bacteria in water. The enterococci, which include Entero-coccus faecalis (E. faecalis), E. faecium, and their varieties are commonly found in the feces of humans and other warm-blooded animals. Although some strains are ubiquitous and not related to fecal pollution, enterococci in water are an indication of fecal pollution and the possible presence of enteric pathogens. These bacteria are found in water and wastewater in a wide range of densities. The detection limit is one colony forming unit (CFU)/volume filtered.
1.2 This test method has been used successfully with temperate fresh and marine ambient waters, and wastewaters. It is the user’s responsibility to ensure the validity of this test method for waters of untested types.
1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are included for information only and are not considered standard.
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. For specific hazard statements, see Section 9.
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
General Information
- Status
- Published
- Publication Date
- 31-Mar-2024
- Technical Committee
- D19 - Water
- Drafting Committee
- D19.24 - Water Microbiology
Relations
- Effective Date
- 01-Apr-2024
- Effective Date
- 01-Apr-2024
- Effective Date
- 01-Apr-2024
- Effective Date
- 01-Apr-2024
- Effective Date
- 01-Apr-2024
Overview
ASTM D5259-24 is the internationally recognized standard test method for the isolation and enumeration of enterococci from water using the membrane filter (MF) procedure. Developed by ASTM International, this standard delivers a validated methodology for detecting and quantifying enterococcus bacteria, which are key indicators of fecal pollution and water quality. The presence of enterococci, such as Enterococcus faecalis, E. faecium, and related species, signals potential contamination by pathogens, thereby assisting in public health protection for potable, shellfish-growing, ambient, and recreational waters.
Key Topics
- Indicator Organisms: Enterococci are significant indicators for evaluating bacteriological water quality. They are linked with the potential presence of enteric pathogens and health outcomes, including swimming-associated gastroenteritis.
- Membrane Filter Technique: A direct count is obtained by filtering water samples, capturing bacteria on a sterile membrane, and incubating the membrane on selective agar media. This method is suitable for a wide range of water volumes and contamination levels, enabling detection down to one colony-forming unit (CFU) per filtered sample.
- Sample Types: Suitable for temperate fresh and marine waters, ambient waters, wastewaters, and validation for untested water types is advised for accurate results.
- Interferences and Limitations: High turbidity or suspended material in samples may hinder filtration and colony counting. Dilution techniques or alternative methods (such as the Most Probable Number, MPN) are recommended if standard filtration cannot be performed.
- Precision and Quality Control: The standard outlines collaborative study data on reproducibility, as well as verification procedures through selective biochemical testing and gram staining, to ensure reliability and specificity.
Applications
The ASTM D5259-24 test method is widely applied for:
- Regulatory Compliance: Used by water utilities and environmental agencies to meet regulatory standards for recreational beaches, drinking water sources, and shellfish-growing waters.
- Public Health Monitoring: Supports epidemiological investigations correlating waterborne pathogens with disease outbreaks, particularly swimming-associated gastrointestinal illnesses.
- Environmental Assessment: Assists in routine monitoring of surface, ground, ambient, and wastewater to detect episodic or chronic fecal contamination.
- Water Treatment Validation: Evaluates the effectiveness of water and wastewater treatment processes by quantifying reductions of enterococci along the treatment chain.
- Research: Used in scientific studies focused on waterborne pathogens, microbial source tracking, and the development of health-based water quality criteria.
Related Standards
- ASTM D1129: Terminology Relating to Water
- ASTM D1193: Specification for Reagent Water
- ASTM D3370: Practices for Sampling Water from Flowing Process Streams
- Standard Methods for the Examination of Water and Wastewater: Referenced for guidance on sample handling and analytic methodologies
- USEPA Guidelines: Microbiological Methods for Monitoring the Environment are often used in conjunction with ASTM D5259-24 for regulatory purposes
By following ASTM D5259-24, laboratories, regulators, and industry professionals can assure accurate, reliable, and reproducible results when testing water for enterococci contamination. The standard serves as a cornerstone for public health activities and regulatory surveillance in water quality management, supporting both national and international environmental protection initiatives.
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Frequently Asked Questions
ASTM D5259-24 is a standard published by ASTM International. Its full title is "Standard Test Method for Isolation and Enumeration of Enterococci from Water by the Membrane Filter Procedure". This standard covers: SIGNIFICANCE AND USE 5.1 The enterococci are indicators of the bacteriological quality for potable water, shellfish growing waters, ambient, and recreational waters. A direct relationship between swimming, associated gastroenteritis, and enterococci has been established through epidemiological studies and marine and fresh water bathing beaches. These studies have led to the development of criteria that can be used to establish bathing water standards based on established health-water quality relationships. 5.2 Since small or large volumes of water or dilutions thereof, can be analyzed by the membrane filter technique, a wide range of levels of enterococci in water can be enumerated and detected. SCOPE 1.1 This test method covers a membrane filter (MF) procedure for the detection and enumeration of the enterococci bacteria in water. The enterococci, which include Entero-coccus faecalis (E. faecalis), E. faecium, and their varieties are commonly found in the feces of humans and other warm-blooded animals. Although some strains are ubiquitous and not related to fecal pollution, enterococci in water are an indication of fecal pollution and the possible presence of enteric pathogens. These bacteria are found in water and wastewater in a wide range of densities. The detection limit is one colony forming unit (CFU)/volume filtered. 1.2 This test method has been used successfully with temperate fresh and marine ambient waters, and wastewaters. It is the user’s responsibility to ensure the validity of this test method for waters of untested types. 1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are included for information only and are not considered standard. 1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. For specific hazard statements, see Section 9. 1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
SIGNIFICANCE AND USE 5.1 The enterococci are indicators of the bacteriological quality for potable water, shellfish growing waters, ambient, and recreational waters. A direct relationship between swimming, associated gastroenteritis, and enterococci has been established through epidemiological studies and marine and fresh water bathing beaches. These studies have led to the development of criteria that can be used to establish bathing water standards based on established health-water quality relationships. 5.2 Since small or large volumes of water or dilutions thereof, can be analyzed by the membrane filter technique, a wide range of levels of enterococci in water can be enumerated and detected. SCOPE 1.1 This test method covers a membrane filter (MF) procedure for the detection and enumeration of the enterococci bacteria in water. The enterococci, which include Entero-coccus faecalis (E. faecalis), E. faecium, and their varieties are commonly found in the feces of humans and other warm-blooded animals. Although some strains are ubiquitous and not related to fecal pollution, enterococci in water are an indication of fecal pollution and the possible presence of enteric pathogens. These bacteria are found in water and wastewater in a wide range of densities. The detection limit is one colony forming unit (CFU)/volume filtered. 1.2 This test method has been used successfully with temperate fresh and marine ambient waters, and wastewaters. It is the user’s responsibility to ensure the validity of this test method for waters of untested types. 1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are included for information only and are not considered standard. 1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. For specific hazard statements, see Section 9. 1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
ASTM D5259-24 is classified under the following ICS (International Classification for Standards) categories: 13.060.70 - Examination of biological properties of water. The ICS classification helps identify the subject area and facilitates finding related standards.
ASTM D5259-24 has the following relationships with other standards: It is inter standard links to ASTM D5259-19, ASTM E3152-23, ASTM E1891-21, ASTM D5465-16(2020), ASTM D6974-20. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.
ASTM D5259-24 is available in PDF format for immediate download after purchase. The document can be added to your cart and obtained through the secure checkout process. Digital delivery ensures instant access to the complete standard document.
Standards Content (Sample)
This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the
Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
Designation: D5259 − 24
Standard Test Method for
Isolation and Enumeration of Enterococci from Water by the
Membrane Filter Procedure
This standard is issued under the fixed designation D5259; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope 2. Referenced Documents
2.1 ASTM Standards:
1.1 This test method covers a membrane filter (MF) proce-
dure for the detection and enumeration of the enterococci D1129 Terminology Relating to Water
D1193 Specification for Reagent Water
bacteria in water. The enterococci, which include Entero-
coccus faecalis (E. faecalis), E. faecium, and their varieties are D3370 Practices for Sampling Water from Flowing Process
Streams
commonly found in the feces of humans and other warm-
blooded animals. Although some strains are ubiquitous and not D3870 Practice for Establishing Performance Characteristics
related to fecal pollution, enterococci in water are an indication for Colony Counting Methods in Microbiology (With-
of fecal pollution and the possible presence of enteric patho- drawn 2000)
gens. These bacteria are found in water and wastewater in a
3. Terminology
wide range of densities. The detection limit is one colony
forming unit (CFU)/volume filtered.
3.1 Definitions:
3.1.1 For definitions of terms used in this standard, refer to
1.2 This test method has been used successfully with
Terminology D1129.
temperate fresh and marine ambient waters, and wastewaters. It
is the user’s responsibility to ensure the validity of this test 3.2 Definitions of Terms Specific to This Standard:
method for waters of untested types.
3.2.1 Enterococcus, n—in this test method, Enterococcus
species are those bacteria that produce red to maroon colonies
1.3 The values stated in SI units are to be regarded as
with black or reddish-brown precipitate on underside, after
standard. The values given in parentheses after SI units are
incubation on mE agar and subsequent transfer to EIA medium.
included for information only and are not considered standard.
3.2.1.1 Discussion—Enterococci include E. faecalis, E.
1.4 This standard does not purport to address all of the
faecium, E. avium, and their variants.
safety concerns, if any, associated with its use. It is the
responsibility of the user of this standard to establish appro-
4. Summary of Test Method
priate safety, health, and environmental practices and deter-
4.1 The procedure given in this test method provides a
mine the applicability of regulatory limitations prior to use.
direct count of bacteria in water based on the development of
For specific hazard statements, see Section 9.
colonies on the surface of the membrane filter. A water sample
1.5 This international standard was developed in accor-
is filtered through the membrane that retains the bacteria.
dance with internationally recognized principles on standard-
Following filtration, the membrane containing the bacterial
ization established in the Decision on Principles for the
cells is placed on a selective, medium, mE agar, and incubated
Development of International Standards, Guides and Recom-
mendations issued by the World Trade Organization Technical
Barriers to Trade (TBT) Committee. 2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
Standards volume information, refer to the standard’s Document Summary page on
the ASTM website.
1 3
This test method is under the jurisdiction of ASTM Committee D19 on Water The last approved version of this historical standard is referenced on
and is the direct responsibility of Subcommittee D19.24 on Water Microbiology. www.astm.org.
Current edition approved April 1, 2024. Published April 2024. Originally Cabelli, V. J., Dufour, A. P., Levin, M. A., McCabe, L. J., and Haberman, P. W.,
approved in 1992. Last previous edition approved in 2019 as D5259 – 19. DOI: “Relationship of Microbial Indicators to Health Effects at Marine Bathing Beaches,”
10.1520/D5259-24. American Journal of Public Health, Vol 69, 1979, pp. 690–696.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D5259 − 24
for 48 h at 41 °C, then transferred to EIA agar and held at 41 °C pump or a syringe equipped with a check valve to prevent the
for 20 min. Enterococci develop as red to maroon colonies with return flow or air, can be used.
black or reddish-brown precipitate on the underside of the
7.10 Flask, filter, vacuum, usually 1 L, with appropriate
filter.
tubing. A filter manifold to hold a number of filter bases is
optional.
5. Significance and Use
7.11 Forceps, straight or curved, with smooth tips to handle
5.1 The enterococci are indicators of the bacteriological
filters without damage.
quality for potable water, shellfish growing waters, ambient,
and recreational waters. A direct relationship between
7.12 Thermometer, checked against a National Institute of
swimming, associated gastroenteritis, and enterococci has been
Standards and Technology (NIST) certified thermometer, or
established through epidemiological studies and marine and
one traceable to an NIST thermometer.
fresh water bathing beaches. These studies have led to the
7.13 Petri Dishes, sterile, plastic, 50 mm by 12 mm, with
development of criteria that can be used to establish bathing
tight-fitting lids.
water standards based on established health-water quality
relationships.
7.14 Bottles, milk dilution, borosilicate glass, screw-cap
with neoprene liners, marked at 99 mL for 1 to 100 dilutions.
5.2 Since small or large volumes of water or dilutions
Dilution bottles marked at 90 mL or tubes marked at 9 mL may
thereof, can be analyzed by the membrane filter technique, a
be used for 1:10 dilutions.
wide range of levels of enterococci in water can be enumerated
and detected.
7.15 Inoculation Loops, at least 3 mm diameter, and
needles, nichrome or platinum wire, 26 B and S gauge, in
6. Interferences
suitable holders.
6.1 Water with high levels of colloidal or suspended mate-
7.16 Incubator maintained at 41 °C 6 0.5 °C.
rials can clog the membrane filter pores and prevent filtration.
Also, suspended materials cause spreading colonies that could
7.17 Waterbath maintained at 44 °C to 46 °C for tempering
interfere with target colonies and thereby prevent accurate
agar.
counting.
7.18 Test Tubes, 150 mm by 20 mm, borosilicate glass or
6.2 Smaller sample size or sample dilution can be used to
plastic.
minimize the interference of turbidity or high-background
7.19 Caps, aluminum or autoclavable plastic, for 20 mm
(non-target) bacterial densities. Replicates of smaller sample
diameter test tubes.
volumes or dilutions of sample may be filtered and the results
combined. If the membrane filter technique is not applicable, 7.20 Test Tubes, screw-cap, borosilicate glass, 125 mm by
the most probable number (MPN) method for fecal strepto-
16 mm or other appropriate size.
cocci is recommended, with verification.
8. Reagents and Materials
6.3 In some samples, chemicals may have toxic effects on
the target organism.
8.1 Purity of Reagents—Reagent grade chemicals shall be
used in all tests. Unless otherwise indicated, it is intended that
7. Apparatus
all reagents conform to the specifications of the Committee on
7.1 Stereoscopic Microscope, wide-field type with magnifi-
Analytical Reagents of the American Chemical Society where
cation of 10× to 15×.
such specifications are available. Other grades may be used,
provided it is first ascertained that the reagent is of sufficiently
7.2 Microscope Lamp, producing diffuse light from a cool,
high purity to permit its use without lessening the accuracy of
white fluorescent lamp adjusted to give maximum visibility.
the determination.
7.3 Counting Device, hand tally or electronic.
8.1.1 The agar used in preparation of culture media must be
7.4 Pipet Container, stainless steel, aluminum, or borosili-
of microbiological grade. Whenever possible, use commercial
cate glass, for glass pipets.
culture media as a means of quality control.
7.5 Pipets, sterile tip delivery bacteriological or Mohr, glass 8.1.2 Purity of Water—Unless otherwise indicated, refer-
or plastic, of appropriate volume. ences to water shall be understood to mean reagent water as
defined by Type III of Specification D1193.
7.6 Graduated Cylinders, 100 mL to 1000 mL, covered with
8.1.3 Ethanol, Methanol or Isopropanol, in a small, wide-
aluminum foil or kraft paper and sterile.
mouth container, for flame-sterilization of pipets.
7.7 Membrane Filtration Units, (filter base and funnel),
glass plastic or stainless steel, wrapped in aluminum foil or
kraft paper and sterilized or disposable sterile plastic units.
ACS Reagent Chemicals, Specifications and Procedures for Reagents and
7.8 Ultraviolet Unit (254 nm), for disinfecting the filtration
Standard-Grade Reference Materials, American Chemical Society, Washington,
unit (optional). DC. For suggestions on the testing of reagents not listed by the American Chemical
Society, see Analar Standards for Laboratory Chemicals, BDH Ltd., Poole, Dorset,
7.9 Line Vacuum, Electric Vacuum Pump, or Aspirator, for
U.K., and the United States Pharmacopeia and National Formulary, U.S. Pharma-
use as a vacuum source. In an emergency or in the field, a hand copeial Convention, Inc. (USPC), Rockville, MD.
D5259 − 24
8.2 Membrane Filters, sterile, white, grid marked, 47 mm 8.6 Brain Heart Infusion (BHI) Broth:
diameter, with 0.45 μm 6 0.02 μm pore size or other pore sizes 8.6.1 Composition:
for which the manufacturer provides data demonstrating
Calf brain infusion 200.0 g
Beef heart infusion 250.0 g
equivalency.
Peptone 10.0 g
8.3 Buffered Dilution Water/Buffered Rinse Water:
Sodium chloride 5.0 g
Disodium phosphate 2.5 g
8.3.1 Composition/Litre:
Dextrose 2.0 g
Sodium dihydrogen phosphate (NaH PO ) 0.58 g
2 4 Water 1000 mL
Sodium monohydrogen phosphate (Na HPO ) 2.50 g
2 4
8.6.2 Preparation—Dissolve 37 g of dehydrated BHI broth
Sodium chloride 8.50 g
in 1 L of water. Dispense in 8 mL to 10 mL volumes in
8.3.2 Preparation—Dissolve the ingredients in 1 L of water
screw-cap tubes and autoclave at 121 °C (15 lb pressure at sea
in a flask and dispense in appropriate amounts for dilutions in
level) for 15 min. If the medium is not used the same day as
screw-cap bottles or culture tubes or into containers for use as
prepared and sterilized, heat in boiling water bath for several
rinse water, or both. Autoclave after preparation at 121 °C
min to remove absorbed oxygen, and cool quickly without
(15 lb pressure at sea level) for 15 min. The final pH should be
agitation, remove absorbed oxygen, and cool quickly without
7.4 6 0.2.
agitation, just prior to inoculation. The final pH should be 7.4
8.4 mE Agar:
6 0.2.
8.4.1 Composition of Basal Medium/Litre:
8.7 BHI Broth with 6.5 % NaCl:
Peptone 10.0 g
8.7.1 Composition—BHI broth with 6.5 % NaCl is the same
Sodium chloride 15.0 g
Yeast extract 30.0 g as BHI broth in 8.6 with additional NaCl.
Esculin 1.0
8.7.2 Preparation—Dissolve 60.0 g NaCl per litre of pre-
Actidione 0.05 g
pared BHI broth. Since most commercially available dehy-
Sodium azide 0.15 g
Agar 15.0 g drated media contain sodium chloride, this amount is taken into
Water 1000 mL
consideration in determining the final NaCl percentage above.
8.4.2 Preparation of Basal Medium—Add 71.2 g of the
8.8 BHI Agar:
above mE basal medium to 1 L of water in a flask and heat to
8.8.1 Composition—BHI agar contains the same compo-
boiling until ingredients dissolve. Autoclave at 121 °C and
nents as BHI (see 8.6) with the addition of 15.0 g of agar per
15 lb pressure for 15 min and cool in a 44 °C to 46 °C water
litre of BHI Broth.
bath.
8.8.2 Preparation—Add 15.0 g of agar and 37.0 g of BHI
8.4.3 Reagents Added After Sterilization—Mix 0.25 g nali-
dehydrated broth to 1 L of water. Heat to boiling until
dixic acid in 5 mL water, add 0.2 mL of NaOH solution
ingredients are dissolved. Dispense 10 mL to 12 mL of medium
(400 g ⁄L) to dissolve, and add to the litre of basal medium. Add
in screw-cap test tubes and sterilize for 15 min at 121 °C (15 lb
0.15 g triphenyl tetrazolium chloride separately to the basal
pressure at sea level). Slant after sterilization. The final pH
medium and mix.
should be 7.4 6 0.2.
8.4.4 Preparation of mE Agar Plates—Pour the mE agar
8.9 Bile Esculin Agar (BEA):
into 50 mm petri plates to a 4 mm to 5 mm depth (approxi-
8.9.1 Composition/Litre:
mately 4 mL to 6 mL), and allow to solidify. The final pH of
B
...
This document is not an ASTM standard and is intended only to provide the user of an ASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation: D5259 − 19 D5259 − 24
Standard Test Method for
Isolation and Enumeration of Enterococci from Water by the
Membrane Filter Procedure
This standard is issued under the fixed designation D5259; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope
1.1 This test method covers a membrane filter (MF) procedure for the detection and enumeration of the enterococci bacteria in
water. The enterococci, which include Entero-coccus faecalis (E. faecalis), E. faecium, and their varieties are commonly found in
the feces of humans and other warm-blooded animals. Although some strains are ubiquitous and not related to fecal pollution,
enterococci in water are an indication of fecal pollution and the possible presence of enteric pathogens. These bacteria are found
in water and wastewater in a wide range of densities. The detection limit is one colony forming unit (CFU)/volume filtered.
1.2 This test method has been used successfully with temperate fresh and marine ambient waters, and wastewaters. It is the user’s
responsibility to ensure the validity of this test method for waters of untested types.
1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses after SI units are included for
information only and are not considered standard.
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of
regulatory limitations prior to use. For specific hazard statements, see Section 9.
1.5 This international standard was developed in accordance with internationally recognized principles on standardization
established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued
by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
2. Referenced Documents
2.1 ASTM Standards:
D1129 Terminology Relating to Water
D1193 Specification for Reagent Water
D3370 Practices for Sampling Water from Flowing Process Streams
D3870 Practice for Establishing Performance Characteristics for Colony Counting Methods in Microbiology (Withdrawn 2000)
3. Terminology
3.1 Definitions:
This test method is under the jurisdiction of ASTM Committee D19 on Water and is the direct responsibility of Subcommittee D19.24 on Water Microbiology.
Current edition approved April 1, 2019April 1, 2024. Published April 2019April 2024. Originally approved in 1992. Last previous edition approved in 20142019 as
D5259 – 14.D5259 – 19. DOI: 10.1520/D5259-19.10.1520/D5259-24.
For referenced ASTM standards, visit the ASTM website, www.astm.org, or contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
The last approved version of this historical standard is referenced on www.astm.org.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D5259 − 24
3.1.1 For definitions of terms used in this standard, refer to Terminology D1129.
3.2 Definitions of Terms Specific to This Standard:
3.2.1 Enterococcus, n—in this test method,Enterococcus species are those bacteria that produce red to maroon colonies with black
or reddish-brown precipitate on underside, after incubation on mE agar and subsequent transfer to EIA medium.
3.2.1.1 Discussion—
Enterococci include E. faecalis, E. faecium, E. avium, and their variants.
4. Summary of Test Method
4.1 The procedure given in this test method provides a direct count of bacteria in water based on the development of colonies on
the surface of the membrane filter. A water sample is filtered through the membrane that retains the bacteria. Following filtration,
the membrane containing the bacterial cells is placed on a selective, medium, mE agar, and incubated for 48 h at 41°C,41 °C, then
transferred to EIA agar and held at 41°C41 °C for 20 min. Enterococci develop as red to maroon colonies with black or
reddish-brown precipitate on the underside of the filter.
5. Significance and Use
5.1 The enterococci are indicators of the bacteriological quality for potable water, shellfish growing waters, ambient, and
recreational waters. A direct relationship between swimming, associated gastroenteritis, and enterococci has been established
through epidemiological studies and marine and fresh water bathing beaches. These studies have led to the development of criteria
that can be used to establish bathing water standards based on established health-water quality relationships.
5.2 Since small or large volumes of water or dilutions thereof, can be analyzed by the membrane filter technique, a wide range
of levels of enterococci in water can be enumerated and detected.
6. Interferences
6.1 Water with high levels of colloidal or suspended materials can clog the membrane filter pores and prevent filtration. Also,
suspended materials cause spreading colonies that could interfere with target colonies and thereby prevent accurate counting.
6.2 Smaller sample size or sample dilution can be used to minimize the interference of turbidity or high-background (non-target)
bacterial densities. Replicates of smaller sample volumes or dilutions of sample may be filtered and the results combined. If the
membrane filter technique is not applicable, the most probable number (MPN) method for fecal streptococci is recommended, with
verification.
6.3 In some samples, chemicals may have toxic effects on the target organism.
7. Apparatus
7.1 Stereoscopic Microscope, wide-field type with magnification of 1010× to 15×.
7.2 Microscope Lamp, producing diffuse light from a cool, white fluorescent lamp adjusted to give maximum visibility.
7.3 Counting Device, hand tally or electronic.
7.4 Pipet Container, stainless steel, aluminum, or borosilicate glass, for glass pipets.
7.5 Pipets, sterile tip delivery bacteriological or Mohr, glass or plastic, of appropriate volume.
Cabelli, V. J., Dufour, A. P., Levin, M. A., McCabe, L. J., and Haberman, P. W., “Relationship of Microbial Indicators to Health Effects at Marine Bathing Beaches,”
American Journal of Public Health, Vol 69, 1979, pp. 690–696.
D5259 − 24
7.6 Graduated Cylinders, 100 to 1000 mL, 100 mL to 1000 mL, covered with aluminum foil or kraft paper and sterile.
7.7 Membrane Filtration Units, (filter base and funnel), glass plastic or stainless steel, wrapped in aluminum foil or kraft paper
and sterilized.sterilized or disposable sterile plastic units.
7.8 Ultraviolet Unit, Unit (254 nm), for disinfecting the filtration unit (optional).
7.9 Line Vacuum, Electric Vacuum Pump, or Aspirator, for use as a vacuum source. In an emergency or in the field, a hand pump
or a syringe equipped with a check valve to prevent the return flow or air, can be used.
7.10 Flask, filter, vacuum, usually 1 L, with appropriate tubing. A filter manifold to hold a number of filter bases is optional.
7.11 Forceps, straight or curved, with smooth tips to handle filters without damage.
7.12 Thermometer, checked against a National Institute of Standards and Technology (NIST) certified thermometer, or one
traceable to an NIST thermometer.
7.13 Petri Dishes, sterile, plastic, 5050 mm by 12 mm, with tight-fitting lids.
7.14 Bottles, milk dilution, borosilicate glass, screw-cap with neoprene liners, marked at 99 mL for 1 to 100 dilutions. Dilution
bottles marked at 90 mL or tubes marked at 9 mL may be used for 1:10 dilutions.
7.15 Inoculation Loops, at least 3-mm3 mm diameter, and needles, nichrome or platinum wire, 26 B and S gage,gauge, in suitable
holders.
7.16 Incubator maintained at 41 6 0.5°C.41 °C 6 0.5 °C.
7.17 Waterbath maintained at 44 to 46°C44 °C to 46 °C for tempering agar.
7.18 Test Tubes, 150150 mm by 20 mm, borosilicate glass or plastic.
7.19 Caps, aluminum or autoclavable plastic, for 20-mm20 mm diameter test tubes.
7.20 Test Tubes, screw-cap, borosilicate glass, 125125 mm by 16 mm or other appropriate size.
8. Reagents and Materials
8.1 Purity of Reagents—Reagent grade chemicals shall be used in all tests. Unless otherwise indicated, it is intended that all
reagents conform to the specifications of the Committee on Analytical Reagents of the American Chemical Society where such
specifications are available. Other grades may be used, provided it is first ascertained that the reagent is of sufficiently high purity
to permit its use without lessening the accuracy of the determination.
8.1.1 The agar used in preparation of culture media must be of microbiological grade. Whenever possible, use commercial culture
media as a means of quality control.
8.1.2 Purity of Water—Unless otherwise indicated, references to water shall be understood to mean reagent water as defined by
Type III of Specification D1193.
Reagent Chemicals, American Chemical Society Specifications,ACS Reagent Chemicals, Specifications and Procedures for Reagents and Standard-Grade Reference
Materials, American Chemical Society, Washington, DC. For suggestions on the testing of reagents not listed by the American Chemical Society, see Analar Standards for
Laboratory Chemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeia and National Formulary, U.S. Pharmacopeial Convention, Inc. (USPC),
Rockville, MD.
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8.1.3 Ethanol, Methanol or Isopropanol, in a small, wide-mouth container, for flame-sterilization of pipets.
8.2 Membrane Filters, sterile, white, grid marked, 47-mm47 mm diameter, with 0.45 6 0.02 μm 0.45 μm 6 0.02 μm pore size or
other pore sizes for which the manufacturer provides data demonstrating equivalency.
8.3 Buffered Dilution Water/Buffered Rinse Water:
8.3.1 Composition/Litre:
Sodium dihydrogen phosphate (NaH PO ) 0.58 g
2 4
Sodium monohydrogen phosphate (Na HPO ) 2.50 g
2 4
Sodium chloride 8.50 g
8.3.2 Preparation—Dissolve the ingredients in 1 L of water in a flask and dispense in appropriate amounts for dilutions in
screw-cap bottles or culture tubes or into containers for use as rinse water, or both. Autoclave after preparation at 121°C (15 lb
121 °C (15 lb pressure at sea level) for 15 min. The final pH should be 7.4 6 0.2.
8.4 mE Agar:
8.4.1 Composition of Basal Medium/Litre:
Peptone 10.0 g
Sodium chloride 15.0 g
Yeast extract 30.0 g
Esculin 1.0
Actidione 0.05 g
Sodium azide 0.15 g
Agar 15.0 g
Water 1000 mL
8.4.2 Preparation of Basal Medium—Add 71.2 g of the above mE basal medium to 1 L of water in a flask and heat to boiling until
ingredients dissolve. Autoclave at 121°C and 15 lb 121 °C and 15 lb pressure for 15 min and cool in a 44 to 46°C44 °C to 46 °C
water bath.
8.4.3 Reagents Added After Sterilization—Mix 0.25 g nalidixic acid in 5 mL water, add 0.2 mL of NaOH solution (400(400 g g/L)
⁄L) to dissolve, and add to the litre of basal medium. Add 0.15 g 0.15 g triphenyl tetrazolium chloride separately to the basal
medium and mix.
8.4.4 Preparation of mE Agar Plates—Pour the mE agar into 50 mm petri plates to a 44 mm to 5 mm depth (approximately 44 mL
to 6 mL), and allow to solidify. The final pH of medium should be 7.1 6 0.2. Store in a refrigerator.
8.5 EIA Agar:
8.5.1 Composition of EIA Medium/Litre:
Esculin 1.0 g
Ferric citrate 0.5 g
Agar 15.0 g
Water 1000 mL
8.5.2 Preparation—Add 16.5 g of dehydrated EIA medium to 1 L of water in flask and heat to boiling until ingredients are
dissolved. Autoclave the EIA medium solution at 121°C121 °C (15 lb pressure at sea level) for 15 min and cool in a 44 to
46°C44 °C to 46 °C water bath. After cooling, pour the medium into 50-mm50 mm petri dishes to a depth of 44 mm to 5 mm
(approximately 44 mL to 6 mL and allow to solidify. The final pH should be 7.1 6 0.2 before autoclaving. Store in a refrigerator.
This is available commercially and is recommended to purchase and not prepare from individual components.
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8.6 Brain Heart Infusion (BHI) Broth:
8.6.1 Composition:
Calf brain infusion 200.0 g
Beef heart infusion 250.0 g
Peptone 10.0 g
Sodium chloride 5.0 g
Disodium phosphate 2.5 g
Dextrose 2.0 g
Water 1000 mL
8.6.2 Preparation—Dissolve 37 g of dehydrated BHI broth in 1 L of water. Dispense in 88 mL to 10 mL volumes in screw-cap
tubes and autoclave at 121°C121 °C (15 lb pressure at sea level) for 15 min. If the medium is not used the same day as prepared
and sterilized, heat in boiling water bath for several min to remove absorbed oxygen, and cool quickly without agitation, remove
absorbed oxygen, and cool quickly without agitation, just prior to inoculation. The final pH sh
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