Standard Test Method for Adenosine Triphosphate (ATP) Content of Microorganisms in Water

SIGNIFICANCE AND USE
5.1 A rapid and routine procedure for determining biomass of the living microorganisms in cultures, waters, wastewaters, and in plankton and periphyton samples taken from surface waters is frequently of vital importance. However, classical techniques such as direct microscope counts, turbidity, organic chemical analyses, cell tagging, and plate counts are expensive, time-consuming, or tend to underestimate total numbers. In addition, some of these methods do not distinguish between living and nonliving cells.  
5.2 This test method measures the concentration of cellular-ATP present in the sample. ATP is a constituent of all living cells, including bacteria, algae, protozoa, and fungi. Consequently, the presence of cellular-ATP is an indicator of total metabolically active microbial contamination in water. ATP is not associated with matter of non-biological origin.  
5.3 The ATP (luciferin-luciferase) method is a rapid, sensitive determination of viable microbial biomass. ATP is the primary energy donor for life processes, does not exist in association with nonliving detrital material, and the amount of ATP per unit of biomass (expressed in weight) is relatively constant. (ATP per cell varies with species and physiological state of the organism.)  
5.4 This test method can be used to:  
5.4.1 Estimate viable microbial biomass in cultures and waters.  
5.4.2 Estimate the amount of total viable biomass in plankton and periphyton samples.  
5.4.3 Estimate the number of viable cells in a unispecies culture if the cATP content (or if the average amount of cATP) per cell is known.  
5.4.4 Estimate and differentiate between zooplanktonic, phytoplanktonic, bacterial, and fungal cATP through size fractionation of water samples.  
5.4.5 Measure the mortality rate of microorganisms in toxicity tests in entrainment studies, and in other situations where populations or assemblages of microorganisms are placed under stress.  
5.5 This test method is similar to Test Metho...
SCOPE
1.1 This test method covers a protocol for capturing, extracting and quantifying the cellular adenosine triphosphate (cATP) content associated with microorganisms normally found in laboratory cultures and waters in plankton and periphyton samples from waters.  
1.2 The ATP is measured using a bioluminescence enzyme assay, whereby light is generated in amounts proportional to the concentration of ATP in the samples. The light is produced and measured quantitatively as relative light units (RLU) which are converted by comparison with an ATP standard and computation to pg ATP/mL.  
1.3 This method does not remove all known chemical interferences, known to either luminesce in the 530 nm ± 20 nm range, or to quench light emitted in that range. It should not be used to determine ATP concentrations in samples with dissolved organic compounds, heavy metals or >10 000 ppm total dissolved solids. Alternative methods have been developed for determining ATP concentrations in fluids samples likely to contain such interferences (Test Methods D7687 and E2694).  
1.4 Knowledge of the concentration of ATP can be related to viable biomass or metabolic activity of microorganisms (Appendix X1).  
1.5 This test method offers a high degree of sensitivity, rapidity, accuracy, and reproducibility.  
1.6 The analyst should be aware that the precision statement pertains only to determinations in reagent water and not necessarily in the matrix being tested.  
1.7 This test method is equally suitable for use in the laboratory or field.  
1.8 The method normally detects cATP concentrations in the range of 0.1 pg cATP/mL (–1.0Log10 [pg cATP/mL]) to
4 000 000 pg cATP/mL (6.6 Log10 [pg cATP/mL]) in 50 mL water samples.  
1.9 Providing interferences can be overcome, bioluminescence is a reliable and proven method for qualifying and quantifying ATP, although the method does not differentiate between ATP from different sources, for example, from...

General Information

Status
Published
Publication Date
31-Oct-2023
Technical Committee
D19 - Water
Drafting Committee
D19.24 - Water Microbiology

Relations

Effective Date
01-Nov-2023
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Overview

ASTM D4012-23a, Standard Test Method for Adenosine Triphosphate (ATP) Content of Microorganisms in Water, establishes a reliable protocol for the rapid quantification of cellular ATP (cATP) in a wide range of water samples. ATP is a universal marker of viable, metabolically active microorganisms, including bacteria, algae, protozoa, and fungi. This method uses a sensitive bioluminescence enzyme assay (luciferin-luciferase reaction) to measure light emitted in proportion to ATP concentration, providing a precise indicator of microbial contamination in laboratory cultures, wastewaters, surface waters, and plankton or periphyton samples.

This test method offers advantages over traditional microbiological techniques, such as direct microscope counting or plate counts, by providing faster, more reproducible, and more accurate results, and by specifically targeting living, active biomass.

Keywords: ATP testing, microbial biomass, water quality, bioluminescence assay, ASTM D4012, cATP, environmental microbiology

Key Topics

  • Test Method Summary: Cellular-ATP is released from microorganisms by lysis, and measured via a bioluminescent reaction whose intensity (in relative light units, RLU) is directly proportional to ATP content, calculated against an ATP standard. Results are reported in picograms ATP per milliliter (pg ATP/mL).
  • Detection Range: The method is highly sensitive, accurately detecting ATP concentrations from 0.1 pg cATP/mL up to 4,000,000 pg cATP/mL in 50 mL water samples.
  • Applicability: Suitable for both field and laboratory applications, covering a broad set of water matrices including fresh, brackish, or marine environments.
  • Advantages Over Classical Methods:
    • Distinguishes between living and dead cells by directly quantifying metabolically active biomass.
    • Faster and less labor-intensive than culturing or microscopy-based techniques.
    • High reproducibility and sensitivity.
  • Limitations and Interference: Not recommended for samples with significant dissolved organic compounds, heavy metals, or high dissolved solids (>10,000 ppm), which may interfere with the bioluminescent assay. For such matrices, alternative ASTM procedures (e.g., D7687, E2694) are advised.
  • Quality Control: Includes calibration, method blanks, laboratory control samples, and batch QC measures to ensure accuracy and consistency, as well as requirements for equipment and reagent purity.

Applications

  • Water Quality Monitoring: Essential for rapid assessment of microbial contamination in municipal, environmental, and industrial water samples.
  • Ecological and Environmental Studies: Used to estimate viable microbial biomass in natural water bodies, including planktonic and periphytic communities.
  • Wastewater Treatment: Provides critical data on microbial activity and bioload, supporting operational efficiency and compliance.
  • Toxicity and Stress Response Testing: Measures reductions in viable microbial ATP as an indicator of organism mortality or metabolic stress during toxicity, entrainment, or ecological impact studies.
  • Microbial Enumeration in Cultures: When the ATP per cell of a target organism is known, the test allows estimation of viable cell numbers in unispecies cultures.
  • Differentiation of Microbial Types: Facilitates assessment and differentiation of zooplanktonic, phytoplanktonic, bacterial, and fungal ATP content through size fractionation.

Related Standards

  • ASTM D7687: Measurement of Cellular Adenosine Triphosphate in Fuel and Fuel-Associated Water
  • ASTM E2694: Measurement of Adenosine Triphosphate in Water-Miscible Metalworking Fluids
  • ASTM D1129: Terminology Relating to Water
  • ASTM D1193: Specification for Reagent Water
  • ASTM E177: Practice for Use of the Terms Precision and Bias in ASTM Test Methods

These related standards offer alternative or complementary methods for ATP measurement in samples with high levels of chemical interference or for process-specific applications.


By integrating rapid, precise ATP testing as outlined in ASTM D4012-23a, laboratories, utilities, and environmental managers can improve microbial water quality assessment, optimize system performance, and respond more swiftly to contamination events.

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Frequently Asked Questions

ASTM D4012-23a is a standard published by ASTM International. Its full title is "Standard Test Method for Adenosine Triphosphate (ATP) Content of Microorganisms in Water". This standard covers: SIGNIFICANCE AND USE 5.1 A rapid and routine procedure for determining biomass of the living microorganisms in cultures, waters, wastewaters, and in plankton and periphyton samples taken from surface waters is frequently of vital importance. However, classical techniques such as direct microscope counts, turbidity, organic chemical analyses, cell tagging, and plate counts are expensive, time-consuming, or tend to underestimate total numbers. In addition, some of these methods do not distinguish between living and nonliving cells. 5.2 This test method measures the concentration of cellular-ATP present in the sample. ATP is a constituent of all living cells, including bacteria, algae, protozoa, and fungi. Consequently, the presence of cellular-ATP is an indicator of total metabolically active microbial contamination in water. ATP is not associated with matter of non-biological origin. 5.3 The ATP (luciferin-luciferase) method is a rapid, sensitive determination of viable microbial biomass. ATP is the primary energy donor for life processes, does not exist in association with nonliving detrital material, and the amount of ATP per unit of biomass (expressed in weight) is relatively constant. (ATP per cell varies with species and physiological state of the organism.) 5.4 This test method can be used to: 5.4.1 Estimate viable microbial biomass in cultures and waters. 5.4.2 Estimate the amount of total viable biomass in plankton and periphyton samples. 5.4.3 Estimate the number of viable cells in a unispecies culture if the cATP content (or if the average amount of cATP) per cell is known. 5.4.4 Estimate and differentiate between zooplanktonic, phytoplanktonic, bacterial, and fungal cATP through size fractionation of water samples. 5.4.5 Measure the mortality rate of microorganisms in toxicity tests in entrainment studies, and in other situations where populations or assemblages of microorganisms are placed under stress. 5.5 This test method is similar to Test Metho... SCOPE 1.1 This test method covers a protocol for capturing, extracting and quantifying the cellular adenosine triphosphate (cATP) content associated with microorganisms normally found in laboratory cultures and waters in plankton and periphyton samples from waters. 1.2 The ATP is measured using a bioluminescence enzyme assay, whereby light is generated in amounts proportional to the concentration of ATP in the samples. The light is produced and measured quantitatively as relative light units (RLU) which are converted by comparison with an ATP standard and computation to pg ATP/mL. 1.3 This method does not remove all known chemical interferences, known to either luminesce in the 530 nm ± 20 nm range, or to quench light emitted in that range. It should not be used to determine ATP concentrations in samples with dissolved organic compounds, heavy metals or >10 000 ppm total dissolved solids. Alternative methods have been developed for determining ATP concentrations in fluids samples likely to contain such interferences (Test Methods D7687 and E2694). 1.4 Knowledge of the concentration of ATP can be related to viable biomass or metabolic activity of microorganisms (Appendix X1). 1.5 This test method offers a high degree of sensitivity, rapidity, accuracy, and reproducibility. 1.6 The analyst should be aware that the precision statement pertains only to determinations in reagent water and not necessarily in the matrix being tested. 1.7 This test method is equally suitable for use in the laboratory or field. 1.8 The method normally detects cATP concentrations in the range of 0.1 pg cATP/mL (–1.0Log10 [pg cATP/mL]) to 4 000 000 pg cATP/mL (6.6 Log10 [pg cATP/mL]) in 50 mL water samples. 1.9 Providing interferences can be overcome, bioluminescence is a reliable and proven method for qualifying and quantifying ATP, although the method does not differentiate between ATP from different sources, for example, from...

SIGNIFICANCE AND USE 5.1 A rapid and routine procedure for determining biomass of the living microorganisms in cultures, waters, wastewaters, and in plankton and periphyton samples taken from surface waters is frequently of vital importance. However, classical techniques such as direct microscope counts, turbidity, organic chemical analyses, cell tagging, and plate counts are expensive, time-consuming, or tend to underestimate total numbers. In addition, some of these methods do not distinguish between living and nonliving cells. 5.2 This test method measures the concentration of cellular-ATP present in the sample. ATP is a constituent of all living cells, including bacteria, algae, protozoa, and fungi. Consequently, the presence of cellular-ATP is an indicator of total metabolically active microbial contamination in water. ATP is not associated with matter of non-biological origin. 5.3 The ATP (luciferin-luciferase) method is a rapid, sensitive determination of viable microbial biomass. ATP is the primary energy donor for life processes, does not exist in association with nonliving detrital material, and the amount of ATP per unit of biomass (expressed in weight) is relatively constant. (ATP per cell varies with species and physiological state of the organism.) 5.4 This test method can be used to: 5.4.1 Estimate viable microbial biomass in cultures and waters. 5.4.2 Estimate the amount of total viable biomass in plankton and periphyton samples. 5.4.3 Estimate the number of viable cells in a unispecies culture if the cATP content (or if the average amount of cATP) per cell is known. 5.4.4 Estimate and differentiate between zooplanktonic, phytoplanktonic, bacterial, and fungal cATP through size fractionation of water samples. 5.4.5 Measure the mortality rate of microorganisms in toxicity tests in entrainment studies, and in other situations where populations or assemblages of microorganisms are placed under stress. 5.5 This test method is similar to Test Metho... SCOPE 1.1 This test method covers a protocol for capturing, extracting and quantifying the cellular adenosine triphosphate (cATP) content associated with microorganisms normally found in laboratory cultures and waters in plankton and periphyton samples from waters. 1.2 The ATP is measured using a bioluminescence enzyme assay, whereby light is generated in amounts proportional to the concentration of ATP in the samples. The light is produced and measured quantitatively as relative light units (RLU) which are converted by comparison with an ATP standard and computation to pg ATP/mL. 1.3 This method does not remove all known chemical interferences, known to either luminesce in the 530 nm ± 20 nm range, or to quench light emitted in that range. It should not be used to determine ATP concentrations in samples with dissolved organic compounds, heavy metals or >10 000 ppm total dissolved solids. Alternative methods have been developed for determining ATP concentrations in fluids samples likely to contain such interferences (Test Methods D7687 and E2694). 1.4 Knowledge of the concentration of ATP can be related to viable biomass or metabolic activity of microorganisms (Appendix X1). 1.5 This test method offers a high degree of sensitivity, rapidity, accuracy, and reproducibility. 1.6 The analyst should be aware that the precision statement pertains only to determinations in reagent water and not necessarily in the matrix being tested. 1.7 This test method is equally suitable for use in the laboratory or field. 1.8 The method normally detects cATP concentrations in the range of 0.1 pg cATP/mL (–1.0Log10 [pg cATP/mL]) to 4 000 000 pg cATP/mL (6.6 Log10 [pg cATP/mL]) in 50 mL water samples. 1.9 Providing interferences can be overcome, bioluminescence is a reliable and proven method for qualifying and quantifying ATP, although the method does not differentiate between ATP from different sources, for example, from...

ASTM D4012-23a is classified under the following ICS (International Classification for Standards) categories: 13.060.50 - Examination of water for chemical substances. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM D4012-23a has the following relationships with other standards: It is inter standard links to ASTM D4012-23, ASTM D6300-24, ASTM D4175-23a, ASTM D6300-23a, ASTM D4175-23, ASTM D4175-23e1, ASTM D6300-23, ASTM D1129-13(2020)e1, ASTM D1129-13(2020)e2, ASTM E2694-21, ASTM D7463-21, ASTM D6469-20, ASTM E645-18, ASTM E1326-20, ASTM D7847-22. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM D4012-23a 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: D4012 − 23a
Standard Test Method for
Adenosine Triphosphate (ATP) Content of Microorganisms
in Water
This standard is issued under the fixed designation D4012; 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 1.9 Providing interferences can be overcome, biolumines-
cence is a reliable and proven method for qualifying and
1.1 This test method covers a protocol for capturing, ex-
quantifying ATP, although the method does not differentiate
tracting and quantifying the cellular adenosine triphosphate
between ATP from different sources, for example, from differ-
(cATP) content associated with microorganisms normally
ent types of microorganisms, such as bacteria, fungi, algae and
found in laboratory cultures and waters in plankton and
protozoa.
periphyton samples from waters.
1.10 The values stated in SI units are to be regarded as
1.2 The ATP is measured using a bioluminescence enzyme
standard. No other units of measurement are included in this
assay, whereby light is generated in amounts proportional to
standard.
the concentration of ATP in the samples. The light is produced
1.11 This standard does not purport to address all of the
and measured quantitatively as relative light units (RLU)
safety concerns, if any, associated with its use. It is the
which are converted by comparison with an ATP standard and
responsibility of the user of this standard to establish appro-
computation to pg ATP/mL.
priate safety, health, and environmental practices and deter-
1.3 This method does not remove all known chemical
mine the applicability of regulatory limitations prior to use.
interferences, known to either luminesce in the 530 nm 6
1.12 This international standard was developed in accor-
20 nm range, or to quench light emitted in that range. It should
dance with internationally recognized principles on standard-
not be used to determine ATP concentrations in samples with
ization established in the Decision on Principles for the
dissolved organic compounds, heavy metals or >10 000 ppm
Development of International Standards, Guides and Recom-
total dissolved solids. Alternative methods have been devel-
mendations issued by the World Trade Organization Technical
oped for determining ATP concentrations in fluids samples
Barriers to Trade (TBT) Committee.
likely to contain such interferences (Test Methods D7687 and
E2694).
2. Referenced Documents
1.4 Knowledge of the concentration of ATP can be related to 2
2.1 ASTM Standards:
viable biomass or metabolic activity of microorganisms (Ap-
D1129 Terminology Relating to Water
pendix X1).
D1193 Specification for Reagent Water
1.5 This test method offers a high degree of sensitivity,
D1601 Test Method for Dilute Solution Viscosity of Ethyl-
rapidity, accuracy, and reproducibility. ene Polymers
D4175 Terminology Relating to Petroleum Products, Liquid
1.6 The analyst should be aware that the precision statement
Fuels, and Lubricants
pertains only to determinations in reagent water and not
D5847 Practice for Writing Quality Control Specifications
necessarily in the matrix being tested.
for Standard Test Methods for Water Analysis
1.7 This test method is equally suitable for use in the
D6161 Terminology Used for Microfiltration, Ultrafiltration,
laboratory or field.
Nanofiltration, and Reverse Osmosis Membrane Processes
1.8 The method normally detects cATP concentrations in the D6300 Practice for Determination of Precision and Bias
range of 0.1 pg cATP/mL (–1.0Log [pg cATP/mL]) to Data for Use in Test Methods for Petroleum Products,
4 000 000 pg cATP/mL (6.6 Log [pg cATP/mL]) in 50 mL Liquid Fuels, and Lubricants
water samples. D7687 Test Method for Measurement of Cellular Adenosine
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. For referenced ASTM standards, visit the ASTM website, www.astm.org, or
Current edition approved Nov. 1, 2023. Published November 2023. Originally contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
approved in 1981. Last previous edition approved in 2023 as D4012 – 23. DOI: Standards volume information, refer to the standard’s Document Summary page on
10.1520/D4012-23A. the ASTM website.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D4012 − 23a
Triphosphate in Fuel and Fuel-associated Water With 3.1.11 luciferase, n—general term for a class of enzymes
Sample Concentration by Filtration that catalyze bioluminescent reactions.
E177 Practice for Use of the Terms Precision and Bias in
3.1.12 luciferin, n—general term for a class of light-emitting
ASTM Test Methods
biological pigments found in organisms capable of biolumi-
E691 Practice for Conducting an Interlaboratory Study to
nescence.
Determine the Precision of a Test Method
3.1.13 luminometer, n—instrument capable of measuring
E2694 Test Method for Measurement of Adenosine Triphos-
light emitted as a result of nonthermal excitation.
phate in Water-Miscible Metalworking Fluids
3.1.14 lysis, n—disintegration or destruction of whole bac-
F1671 Test Method for Resistance of Materials Used in
terial cells. F1671
Protective Clothing to Penetration by Blood-Borne Patho-
gens Using Phi-X174 Bacteriophage Penetration as a Test
3.1.15 relative light unit (RLU), n—instrument and assay
System specific unit of measurement reflecting the number of photons
emitted by the Luciferin-Luciferase driven hydrolysis of ATP
3. Terminology to AMP plus pyrophosphate.
3.1.15.1 Discussion—RLU is not an SI unit, however, RLU
3.1 Definitions:
are proportional to ATP concentration.
3.1.1 For definitions of terms used in this standard, refer to
3.1.16 viable microbial biomass, n—metabolically active
Terminologies D1129 and D4175.
(living) microorganisms.
3.1.2 adenosine monophosphate (AMP), n—molecule
formed by the removal of two molecules of phosphate (one
3.2 Acronyms:
pyrophosphate molecule) from ATP.
3.2.1 AMP, n—adenosine monophosphate.
3.1.3 adenosine triphosphate (ATP), n—molecule com-
3.2.2 ATP, n—adenosine triphosphate.
prised of a purine and three phosphate groups that serves as the
3.2.3 HDPE, n—high density polyethylene.
primary energy transport molecule in all biological cells.
3.2.4 PP, n—polypropylene.
3.1.4 aseptic, adj—sterile, free from viable microbial con-
-12
3.2.5 pg, n—picogram (1 × 10 g).
tamination.
3.2.6 RLU, n—relative light unit.
3.1.5 background RLU, n—quantity of relative light units
resulting from running the test method without incorporation of
4. Summary of Test Method
the sample.
4.1 A control assay is performed using 100 μL of 1.0 ng 6
3.1.6 bioluminescence, n—production and emission of light
0.05 ng ATP/mL standard to produce RLU .
ctrl
by a living organism as the result of a chemical reaction during
which chemical energy is converted to light energy. 4.2 A 50 mL sample of water is placed into a syringe and
then pressure-filtered through a 0.7 μm, glass-fiber, in-line,
3.1.7 biomass, n—any matter which is or was a living
depth filter.
organism or excreted from a microorganism. D6161
4.3 A lysing reagent is used to release cellular-ATP from
3.1.8 cellular adenosine triphosphate (cellular-ATP;
microbial cells that have been captured on the glass-fiber filter,
c-ATP), n—ATP present in whole cells, whether they are living
and the filtrate is dispensed into an unused culture tube.
or dead.
3.1.8.1 Discussion—Cellular-ATP is released upon inten-
4.4 The filtrate is diluted 1 to 10 with a buffer solution.
tional lysis of microbial cells during the sample preparation
4.5 A 100 μL volume of diluted filtrate is transferred to an
process. Microbially infected fluids contain both cellular (cell-
unused culture tube into which 100 μL of Luciferin-Luciferase
associated/cell-bound) and extra-cellular ATP.
reagent has been previously dispensed.
3.1.9 culturable, adj—(microorganisms that are) able to
4.6 The culture tube is placed into a luminometer and the
proliferate as indicated by the formation of colonies on solid
light intensity is read as RLU .
obs
growth media or the development of turbidity in liquid growth
4.7 RLU is normalized to an actual pg ATP/mL concen-
media under specific growth conditions.
obs
tration through an equation that accounts for the result of the
3.1.10 extra-cellular, adj—(molecules or substances that are
control assay (RLU ), the volume of the sample processed,
ctrl
either) excreted by living cells or released from microbial cells
and the method dilution factor.
that have lysed (see 3.1.14) in the sample.
3.1.10.1 Discussion—Extra-cellular ATP is ATP that has NOTE 1—Optionally, for condition monitoring purposes, pg ATP/mL are
converted to Log [pg ATP/mL] of sample by computation.
been released from microbial cells that have either fully or 10
partially lysed in the sample, the upstream fluid (fuel or water
5. Significance and Use
phase), or both.
3.1.10.2 Discussion—Lysis can occur due to natural life 5.1 A rapid and routine procedure for determining biomass
cycle process, antimicrobial treatment or a combination of of the living microorganisms in cultures, waters, wastewaters,
these factors. Extra-cellular ATP can under certain circum- and in plankton and periphyton samples taken from surface
stances persist for periods greater than 24 h after cell lysis waters is frequently of vital importance. However, classical
depending on physical/chemical conditions. techniques such as direct microscope counts, turbidity, organic
D4012 − 23a
chemical analyses, cell tagging, and plate counts are expensive, 5.6.2.3 The greater the total bioburden, the greater the ATP
time-consuming, or tend to underestimate total numbers. In concentration in a sample.
addition, some of these methods do not distinguish between
6. Interferences
living and nonliving cells.
5.2 This test method measures the concentration of cellular- 6.1 Reagents must be of high purity so that background light
emission is held to a minimum for the measurement of ATP.
ATP present in the sample. ATP is a constituent of all living
cells, including bacteria, algae, protozoa, and fungi.
6.2 ATP-free glassware, prepared by the procedure in 7.5, is
Consequently, the presence of cellular-ATP is an indicator of
required for the determination of ATP.
total metabolically active microbial contamination in water.
6.3 Luciferase is a protein and as such can be inhibited or
ATP is not associated with matter of non-biological origin.
denatured through the presence of heavy metals, high salt (for
5.3 The ATP (luciferin-luciferase) method is a rapid, sensi-
example, NaCl) concentrations, and organic solvents in the
tive determination of viable microbial biomass. ATP is the
sample. Additionally, high amounts of color or turbidity in the
primary energy donor for life processes, does not exist in
sample can impede light transmission, causing a negative bias.
association with nonliving detrital material, and the amount of
Although the method described herein is designed to mitigate
ATP per unit of biomass (expressed in weight) is relatively
such interferences in most types of water, for samples with
constant. (ATP per cell varies with species and physiological
high amounts of such interferences consider the use of Test
state of the organism.)
Methods D7687 and E2694.
5.4 This test method can be used to:
6.4 Other energy-mediating compounds, such as adenosine
5.4.1 Estimate viable microbial biomass in cultures and
diphosphate, cytidine-5-triphosphate, and inosine-5-
waters.
triphosphate also react with luciferase to produce light, but as
5.4.2 Estimate the amount of total viable biomass in plank-
compared to ATP they are usually present only in small
ton and periphyton samples.
amounts and do not constitute a significant source of error.
5.4.3 Estimate the number of viable cells in a unispecies
culture if the cATP content (or if the average amount of cATP)
7. Apparatus
per cell is known.
7.1 Culture Tube, sterile, disposable, PP, 12 mm by 55 mm.
5.4.4 Estimate and differentiate between zooplanktonic,
7.2 Culture Tube, sterile, disposable, PP, 17 mm by 100 mm
phytoplanktonic, bacterial, and fungal cATP through size
with caps.
fractionation of water samples.
5.4.5 Measure the mortality rate of microorganisms in
7.3 Filter, 25 mm, sterile, disposable, PP housing, in-line,
toxicity tests in entrainment studies, and in other situations
0.7 μm pore-size, glass-fiber depth-type with Luer-Lok inlet.
where populations or assemblages of microorganisms are
7.4 Luminometer, using photomultiplier tube, having a
placed under stress.
spectral range between 300 nm and 600 nm, and with a cuvette
5.5 This test method is similar to Test Methods D7687 and
chamber that can hold and provide an unobstructed line of sight
E2694 except for the volumes sampled, and omission of wash
to the reactants in a 12 mm by 55 mm test culture tube (7.1),
and drying steps used in Test Methods D7687 and E2694 to
providing a ratio of RLU /RLU (refer to Section 10
background ctrl
remove interferences (1.3).
and Appendix X5) ≤0.01 and optimally having five decades of
linearity (refer to Appendix X2).
5.6 Although ATP data generally covary with culture data in
water samples, different factors affect cATP concentration than
NOTE 2—It is the responsibility of the user to ensure that the
those that affect culturability.
luminometer selected for use meets the criteria listed in 7.4 and to consult
5.6.1 Culturability is affected primarily by the ability of with the luminometer manufacturer to ensure that use of the luminometer
with the apparatus, reagents and materials described in Sections 6 and 7
captured microbes to proliferate on the growth medium
does not result in the inability of the instrument manufacturer to provide
provided, under specific growth conditions. Consequently, a
technical support or loss of instrument warranty.
proportion of the active or inactive microbial population
NOTE 3—The preliminary interlaboratory study and data presented in
present in a sample may be viable but not detected by any one
Table X4.2, respectively, were developed using a Kikkoman Lumitester
3 4
culture test. C-110, which provides nominally a 5000 RLU and 50 RLU .
ctrl background
Although this test method is optimized to function on this luminometer,
5.6.2 ATP concentration is affected by: the microbial spe-
users may examine the use of other luminometers according to key
cies present, the physiological states of those species, and the
performance criteria, including linear measurement range (Appendix X2)
total bioburden (see Appendix X1).
and RLU level (Appendix X5).
background
5.6.2.1 One example of the species effect is that the amount
7.5 Macropipeter, adjustable, 1.0 mL to 5.0 mL.
of ATP per cell is substantially greater for active fungal cells
7.6 Micropipeter, adjustable, 100 μL to 1000 μL.
than bacteria (Appendix X1).
5.6.2.2 Within a species, cells that are more metabolically
active will have more ATP per cell than dormant cells, such as
fungal spores. The sole source of supply of the Kikkoman Lumitester C-110 apparatus known
to the committee at this time is Hach Company, Colorado. If you are aware of
alternative suppliers, please provide this information to ASTM International
Sloan, W. T., Quince, C., and Curtis, T. P., “The Uncountables,” Accessing Headquarters. Your comments will receive careful consideration at a meeting of the
Uncultivated Microorganisms, ASM Press, Washington, DC, 2008, p. 35. responsible technical committee, which you may attend.
D4012 − 23a
7.7 Pipet Tips, sterile, disposable, PP, 100 μL to 1000 μL. operated in explosive atmospheres or in locations where there
may be explosive fumes, as it cannot be grounded. Consult the
7.8 Pipet Tips, sterile, disposable, PP, 1.0 mL to 5.0 mL.
manufacturer’s guidelines for further information.
7.9 Sample Collection Container, sterile, wide-mouth
bottle, PP or HDPE, 100 mL.
10. Precaution
NOTE 4—ATP can adsorb onto glass surfaces. Consequently, PP or 10.1 This standard may involve the use of hazardous
HDPE containers are strongly preferred.
materials, operations, and equipment. It is the responsibility of
whoever uses this standard to establish appropriate safety
7.10 Syringe, Luer-Lok, 60 mL, PP, sterile disposable.
practices and to determine the applicability of regulatory
7.11 Test Tube Rack, 12 mm.
limitations prior to use.
7.12 Test Tube Rack, 17 mm.
11. Sample Collection
7.13 Waste Receptacle, any container suitable for receiving
and retaining filtrate fluid for ultimate disposal. 11.1 The sample sites should correspond as closely as
possible to those selected for chemical, biological, and micro-
8. Reagents and Materials
biological sampling, so that there is maximum correlation of
results. The sample collection method will be determined by
8.1 Purity of Reagents—Reagent grade chemicals shall be
study objectives. To collect a sample, use a nonmetallic water
used in all tests. Unless otherwise indicated, it is intended that
sampling bottle. Extraction procedures should be performed
all reagents shall conform to the specifications of the Commit-
immediately after collection. The sample may be stored 2 h to
tee on Analytical Reagents of the American Chemical Society,
3 h if necessary if the temperature and lighting conditions are
where such specifications are available. Other grades may be
maintained; for example, do not place a warm sample from a
used, provided it is first ascertained that the reagent is of
well-lighted area into a cool, dark ice chest.
sufficiently high purity to permit its use without lessening the
accuracy of the determination.
12. Calibration and Standardization
8.2 Purity of Water—Unless otherwise indicated, references
12.1 It is necessary to perform only one calibration during
to water shall conform to Specification D1193, Type II.
each set of tests performed on the same day, using the same
8.3 ATP Standard Solution, 1.0 ng 6 0.05 ng ATP/mL—
reagent batches, under the same temperature, using the same
Weigh 119.3 mg of crystalline adenosine 5'-triphosphate-
materials and the same luminometer. In general, one calibration
disodium salt using ATP-free glassware. Dissolve the ATP in
per day of testing is sufficient so long as the aforementioned
100 mL of fresh 0.02 M tris buffer containing 29.2 mg of
variables are kept the same.
EDTA (Na H EDTA·2H O) and 120 mg of MgSO (the
2 2 2 4
NOTE 6—Although multi-point calibration is not required, guidance on
resulting concentration is 1 mg of ATP/mL). The material may
performing a multi-point calibration is provided in Appendix X2.
be dispensed in 1.0-mL aliquots and stored at –20 °C until
12.2 Turn on power to luminometer (6.4) and allow instru-
required.
ment to equilibrate, in accordance with manufacturer’s recom-
8.4 ATP Extract Dilution Buffer, (proprietary).
mendations.
8.5 ATP Extraction Reagent, (proprietary).
12.2.1 It is possible, that during prolonged use, over the
course of several hours, some luminometer models will heat up
8.6 Luciferin-Luciferase Reagent, (proprietary). Store be-
sufficiently to affect the temperature of the reactants (13.25) to
tween –20 °C and 4 °C; allow to equilibrate to ambient
affect the test result (13.25). Excessive on-time can also
temperature before using.
stimulate the photomultiplier tube to produce increased instru-
NOTE 5—Follow manufacturers’ instructions regarding product storage
ment background noise. Consequently, it is advisable to repeat
and shelf life.
12.6 – 12.9 after every 3 h of continuous operation.
9. Hazards 12.3 Ensure that all reagents have equilibrated to ambient
temperature (22 °C 6 3 °C) before running any tests.
9.1 Warning—Not all luminometers are explosion proof.
Luminometers that are not explosion-proof should not be
NOTE 7—The kinetics of the enzymatic reaction measured by this
procedure are affected by temperature.
12.3.1 It is important to ensure that the assay is performed
ACS Reagent Chemicals, Specifications and Procedures for Reagents and
at constant temperature (T 6 3 °C), that is, the instrument and
Standard-Grade Reference Materials, American Chemical Society, Washington,
all reagents must remain at same temperature during the
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,
measurement series.
U.K., and the United States Pharmacopeia and National Formulary, U.S. Pharma-
12.3.2 If the measurement results are to be compared to a
copeial Convention, Inc. (USPC), Rockville, MD.
6 standard curve or control samples these must be measured at
The sole source of supply of the proprietary ATP dilution buffer, ATP extraction
the same conditions and temperature as the test sample.
reagent, filter wash reagent, and Luciferin-Luciferase reagent, is LuminUltra
Technologies Ltd., Fredericton, New Brunswick, Canada, http://
12.3.3 Changes in the instrument, diluted sample (13.19)
www.luminultra.com. If you are aware of alternative suppliers, please provide this
ATP standard (8.3) or Luciferin-Luciferase reagent (8.6) tem-
information to ASTM International Headquarters. Your comments will receive
perature while testing multiple samples will affect the RLU and
careful consideration at a meeting of the responsible technical committee, which
you may attend. consequently introduce a bias to the test results.
D4012 − 23a
12.4 Use a micropipeter (7.6) with a new 100 μL to 1000 μL 13.15 While holding the barrel over the 17 mm by 100 mm
tip (7.7) to dispense 100 μL Luciferin-Luciferase reagent (8.6) culture tube (13.12), replace the 60 mL syringe plunger.
to an unused 12 mm by 55 mm culture tube (7.1).
13.16 Apply even pressure to the 60 mL syringe plunger, to
12.5 Replace the micropipeter tip with a fresh 100 μL to dispense ATP Extraction Reagent and extracted ATP into the
1000 μL tip. 17 mm by 100 mm culture tube.
12.6 Dispense 100 μL of 1 ng ATP/mL standard solution
NOTE 8—At this point in the protocol, this ATP extract may be stored
for up to seven days at 2 °C to 8 °C prior to completing the test.
(8.3) into the culture tube.
13.17 If not already performed (12.2), turn power on lumi-
12.7 Swirl gently for five times.
nometer (7.4) and allow instrument to equilibrate, in accor-
12.8 Place the culture tube into the luminometer.
dance with manufacturer’s recommendations.
12.9 Read and record RLU (RLU ).
ctrl
13.18 Place a fresh 1.0 mL to 5.0 mL pipet tip onto the
macropipeter.
13. ATP Measurement Procedure
13.19 Use macropipeter to dispense two 4.5 mL portions
13.1 Use aseptic procedure while performing this test
(9.0 mL total) of ATP extract dilution buffer (8.4) into the
method; cellular-ATP from analyst’s hands, sputum, etc., can
culture tube to prepare diluted ATP extract.
contaminate the sample with cellular-ATP from sources other
than the sample itself.
13.20 Place cap on culture tube and invert three times to
mix well.
13.2 Remove plunger from a new 60 mL syringe (7.10) and
place onto 17 mm test tube rack so that plunger tip does not
NOTE 9—Diluted ATP extract is stable for up to 4 h at room temperature
contact any surfaces so as to avoid contamination with ATP
...


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: D4012 − 23 D4012 − 23a
Standard Test Method for
Adenosine Triphosphate (ATP) Content of Microorganisms
in Water
This standard is issued under the fixed designation D4012; 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 protocol for capturing, extracting and quantifying the cellular adenosine triphosphate (cATP) content
associated with microorganisms normally found in laboratory cultures and waters in plankton and periphyton samples from waters.
1.2 The ATP is measured using a bioluminescence enzyme assay, whereby light is generated in amounts proportional to the
concentration of ATP in the samples. The light is produced and measured quantitatively as relative light units (RLU) which are
converted by comparison with an ATP standard and computation to pg ATP/mL.
1.3 This method does not remove all known chemical interferences, known to either luminesce in the 530 nm 6 20 nm range, or
to quench light emitted in that range. It should not be used to determine ATP concentrations in samples with dissolved organic
compounds, heavy metals or >10 000 ppm total dissolved solids. Alternative methods have been developed for determining ATP
concentrations in fluids samples likely to contain such interferences (Test Methods D7687 and E2694).
1.4 Knowledge of the concentration of ATP can be related to viable biomass or metabolic activity of microorganisms (Appendix
X1).
1.5 This test method offers a high degree of sensitivity, rapidity, accuracy, and reproducibility.
1.6 The analyst should be aware that the precision statement pertains only to determinations in reagent water and not necessarily
in the matrix being tested.
1.7 This test method is equally suitable for use in the laboratory or field.
1.8 The method normally detects cATP concentrations in the range of 0.1 pg cATP/mL (–1.0Log [pg cATP/mL]) to
4 000 000 pg cATP/mL (6.6 Log [pg cATP/mL]) in 50 mL water samples.
1.9 Providing interferences can be overcome, bioluminescence is a reliable and proven method for qualifying and quantifying ATP,
although the method does not differentiate between ATP from different sources, for example, from different types of
microorganisms, such as bacteria, fungi, algae and protozoa.
1.10 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.
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 July 1, 2023Nov. 1, 2023. Published August 2023November 2023. Originally approved in 1981. Last previous edition approved in 20152023
as D4012 – 15.D4012 – 23. DOI: 10.1520/D4012-23.10.1520/D4012-23A.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D4012 − 23a
1.11 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.
1.12 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
D1601 Test Method for Dilute Solution Viscosity of Ethylene Polymers
D4175 Terminology Relating to Petroleum Products, Liquid Fuels, and Lubricants
D5847 Practice for Writing Quality Control Specifications for Standard Test Methods for Water Analysis
D6161 Terminology Used for Microfiltration, Ultrafiltration, Nanofiltration, and Reverse Osmosis Membrane Processes
D6300 Practice for Determination of Precision and Bias Data for Use in Test Methods for Petroleum Products, Liquid Fuels, and
Lubricants
D7687 Test Method for Measurement of Cellular Adenosine Triphosphate in Fuel and Fuel-associated Water With Sample
Concentration by Filtration
E177 Practice for Use of the Terms Precision and Bias in ASTM Test Methods
E691 Practice for Conducting an Interlaboratory Study to Determine the Precision of a Test Method
E2694 Test Method for Measurement of Adenosine Triphosphate in Water-Miscible Metalworking Fluids
F1671 Test Method for Resistance of Materials Used in Protective Clothing to Penetration by Blood-Borne Pathogens Using
Phi-X174 Bacteriophage Penetration as a Test System
3. Terminology
3.1 Definitions:
3.1.1 For definitions of terms used in this standard, refer to Terminologies D1129 and D4175.
3.1.2 adenosine monophosphate (AMP), n—molecule formed by the removal of two molecules of phosphate (one pyrophosphate
molecule) from ATP.
3.1.3 adenosine triphosphate (ATP), n—molecule comprised of a purine and three phosphate groups that serves as the primary
energy transport molecule in all biological cells.
3.1.4 aseptic, adj—sterile, free from viable microbial contamination.
3.1.5 background RLU, n—quantity of relative light units resulting from running the test method without incorporation of the
sample.
3.1.6 bioluminescence, n—production and emission of light by a living organism as the result of a chemical reaction during which
chemical energy is converted to light energy.
3.1.7 biomass, n—any matter which is or was a living organism or excreted from a microorganism. D6161
3.1.8 cellular adenosine triphosphate (cellular-ATP; c-ATP), n—ATP present in whole cells, whether they are living or dead.
3.1.8.1 Discussion—
Cellular-ATP is released upon intentional lysis of microbial cells during the sample preparation process. Microbially infected fluids
contain both cellular (cell-associated/cell-bound) and extra-cellular ATP.
3.1.9 culturable, adj—(microorganisms that are) able to proliferate as indicated by the formation of colonies on solid growth
media or the development of turbidity in liquid growth media under specific growth conditions.
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.
D4012 − 23a
3.1.10 extra-cellular, adj—(molecules or substances that are either) excreted by living cells or released from microbial cells that
have lysed (see 3.1.14) in the sample.
3.1.10.1 Discussion—
Extra-cellular ATP is ATP that has been released from microbial cells that have either fully or partially lysed in the sample, the
upstream fluid (fuel or water phase), or both.
3.1.10.2 Discussion—
Lysis can occur due to natural life cycle process, antimicrobial treatment or a combination of these factors. Extra-cellular ATP can
under certain circumstances persist for periods greater than 24 h after cell lysis depending on physical/chemical conditions.
3.1.11 luciferase, n—general term for a class of enzymes that catalyze bioluminescent reactions.
3.1.12 luciferin, n—general term for a class of light-emitting biological pigments found in organisms capable of bioluminescence.
3.1.13 luminometer, n—instrument capable of measuring light emitted as a result of nonthermal excitation.
3.1.14 lysis, n—disintegration or destruction of whole bacterial cells. F1671
3.1.15 relative light unit (RLU), n—instrument and assay specific unit of measurement reflecting the number of photons emitted
by the Luciferin-Luciferase driven hydrolysis of ATP to AMP plus pyrophosphate.
3.1.15.1 Discussion—
RLU is not an SI unit, however, RLU are proportional to ATP concentration.
3.1.16 viable microbial biomass, n—metabolically active (living) microorganisms.
3.2 Acronyms:
3.2.1 AMP, n—adenosine monophosphate.
3.2.2 ATP, n—adenosine triphosphate.
3.2.3 HDPE, n—high density polyethylene.
3.2.4 PP, n—polypropylene.
-12
3.2.5 pg, n—picogram (1 × 10 g).
3.2.6 RLU, n—relative light unit.
4. Summary of Test Method
4.1 A control assay is performed using 100 μL of 1.0 ng 6 0.05 ng ATP/mL standard to produce RLU .
ctrl
4.2 A 50 mL sample of water is placed into a syringe and then pressure-filtered through a 0.7 μm, glass-fiber, in-line, depth filter.
4.3 A lysing reagent is used to release cellular-ATP from microbial cells that have been captured on the glass-fiber filter, and the
filtrate is dispensed into an unused culture tube.
4.4 The filtrate is diluted 1 to 10 with a buffer solution.
4.5 A 100 μL volume of diluted filtrate is transferred to an unused culture tube into which 100 μL of Luciferin-Luciferase reagent
has been previously dispensed.
4.6 The culture tube is placed into a luminometer and the light intensity is read as RLU .
obs
D4012 − 23a
4.7 RLU is normalized to an actual pg ATP/mL concentration through an equation that accounts for the result of the control
obs
assay (RLU ), the volume of the sample processed, and the method dilution factor.
ctrl
NOTE 1—Optionally, for condition monitoring purposes, pg ATP/mL are converted to Log [pg ATP/mL] of sample by computation.
5. Significance and Use
5.1 A rapid and routine procedure for determining biomass of the living microorganisms in cultures, waters, wastewaters, and in
plankton and periphyton samples taken from surface waters is frequently of vital importance. However, classical techniques such
as direct microscope counts, turbidity, organic chemical analyses, cell tagging, and plate counts are expensive, time-consuming,
or tend to underestimate total numbers. In addition, some of these methods do not distinguish between living and nonliving cells.
5.2 This test method measures the concentration of cellular-ATP present in the sample. ATP is a constituent of all living cells,
including bacteria, algae, protozoa, and fungi. Consequently, the presence of cellular-ATP is an indicator of total metabolically
active microbial contamination in water. ATP is not associated with matter of non-biological origin.
5.3 The ATP (luciferin-luciferase) method is a rapid, sensitive determination of viable microbial biomass. ATP is the primary
energy donor for life processes, does not exist in association with nonliving detrital material, and the amount of ATP per unit of
biomass (expressed in weight) is relatively constant. (ATP per cell varies with species and physiological state of the organism.)
5.4 This test method can be used to:
5.4.1 Estimate viable microbial biomass in cultures and waters.
5.4.2 Estimate the amount of total viable biomass in plankton and periphyton samples.
5.4.3 Estimate the number of viable cells in a unispecies culture if the cATP content (or if the average amount of cATP) per cell
is known.
5.4.4 Estimate and differentiate between zooplanktonic, phytoplanktonic, bacterial, and fungal cATP through size fractionation of
water samples.
5.4.5 Measure the mortality rate of microorganisms in toxicity tests in entrainment studies, and in other situations where
populations or assemblages of microorganisms are placed under stress.
5.5 This test method is similar to Test Methods D7687 and E2694 except for the volumes sampled, and omission of wash and
drying steps used in Test Methods D7687 and E2694 to remove interferences (1.3).
5.6 Although ATP data generally covary with culture data in water samples, different factors affect cATP concentration than those
that affect culturability.
5.6.1 Culturability is affected primarily by the ability of captured microbes to proliferate on the growth medium provided, under
specific growth conditions. Consequently, a proportion of the active or inactive microbial population present in a sample may be
viable but not detected by any one culture test.
5.6.2 ATP concentration is affected by: the microbial species present, the physiological states of those species, and the total
bioburden (see Appendix X1).
5.6.2.1 One example of the species effect is that the amount of ATP per cell is substantially greater for active fungal cells than
bacteria (Appendix X1).
5.6.2.2 Within a species, cells that are more metabolically active will have more ATP per cell than dormant cells, such as fungal
spores.
Sloan, W. T., Quince, C., and Curtis, T. P., “The Uncountables,” Accessing Uncultivated Microorganisms, ASM Press, Washington, DC, 2008, p. 35.
D4012 − 23a
5.6.2.3 The greater the total bioburden, the greater the ATP concentration in a sample.
6. Interferences
6.1 Reagents must be of high purity so that background light emission is held to a minimum for the measurement of ATP.
6.2 ATP-free glassware, prepared by the procedure in 7.5, is required for the determination of ATP.
6.3 Luciferase is a protein and as such can be inhibited or denatured through the presence of heavy metals, high salt (for example,
NaCl) concentrations, and organic solvents in the sample. Additionally, high amounts of color or turbidity in the sample can impede
light transmission, causing a negative bias. Although the method described herein is designed to mitigate such interferences in most
types of water, for samples with high amounts of such interferences consider the use of Test Methods D7687 and E2694.
6.4 Other energy-mediating compounds, such as adenosine diphosphate, cytidine-5-triphosphate, and inosine-5-triphosphate also
react with luciferase to produce light, but as compared to ATP they are usually present only in small amounts and do not constitute
a significant source of error.
7. Apparatus
7.1 Culture Tube, sterile, disposable, PP, 12 mm by 55 mm.
7.2 Culture Tube, sterile, disposable, PP, 17 mm by 100 mm with caps.
7.3 Filter, 25 mm, sterile, disposable, PP housing, in-line, 0.7 μm pore-size, glass-fiber depth-type with Luer-Lok inlet.
7.4 Luminometer, using photomultiplier tube, having a spectral range between 300 nm and 600 nm, and with a cuvette chamber
that can hold and provide an unobstructed line of sight to the reactants in a 12 mm by 55 mm test culture tube (7.1), providing
a ratio of RLU /RLU (refer to Section 10 and Appendix X5) ≤0.01 and optimally having five decades of linearity (refer
background ctrl
to Appendix X2).
NOTE 2—It is the responsibility of the user to ensure that the luminometer selected for use meets the criteria listed in 7.4 and to consult with the
luminometer manufacturer to ensure that use of the luminometer with the apparatus, reagents and materials described in Sections 6 and 7 does not result
in the inability of the instrument manufacturer to provide technical support or loss of instrument warranty.
NOTE 3—The preliminary interlaboratory study and data presented in Table X4.2, respectively, were developed using a Kikkoman Lumitester C-110,
which provides nominally a 5000 RLU and 50 RLU . Although this test method is optimized to function on this luminometer, users may
ctrl background
examine the use of other luminometers according to key performance criteria, including linear measurement range (Appendix X2) and RLU level
background
(Appendix X5).
7.5 Macropipeter, adjustable, 1.0 mL to 5.0 mL.
7.6 Micropipeter, adjustable, 100 μL to 1000 μL.
7.7 Pipet Tips, sterile, disposable, PP, 100 μL to 1000 μL.
7.8 Pipet Tips, sterile, disposable, PP, 1.0 mL to 5.0 mL.
7.9 Sample Collection Container, sterile, wide-mouth bottle, PP or HDPE, 100 mL.
NOTE 4—ATP can adsorb onto glass surfaces. Consequently, PP or HDPE containers are strongly preferred.
The sole source of supply of the Kikkoman Lumitester C-110 apparatus known to the committee at this time is Hach Company, Colorado. If you are aware of alternative
suppliers, please provide this information to ASTM International Headquarters. Your comments will receive careful consideration at a meeting of the responsible technical
committee, which you may attend.
D4012 − 23a
7.10 Syringe, Luer-Lok, 60 mL, PP, sterile disposable.
7.11 Test Tube Rack, 12 mm.
7.12 Test Tube Rack, 17 mm.
7.13 Waste Receptacle, any container suitable for receiving and retaining filtrate fluid for ultimate disposal.
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 shall 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.
8.2 Purity of Water—Unless otherwise indicated, references to water shall conform to Specification D1193, Type II.
8.3 ATP Standard Solution, 1.0 ng 6 0.05 ng ATP/mL—Weigh 119.3 mg of crystalline adenosine 5'-triphosphate-disodium salt
using ATP-free glassware. Dissolve the ATP in 100 mL of fresh 0.02 M tris buffer containing 29.2 mg of EDTA (Na H
2 2
EDTA·2H O) and 120 mg of MgSO (the resulting concentration is 1 mg of ATP/mL). The material may be dispensed in 1.0-mL
2 4
aliquots and stored at –20 °C until required.
8.4 ATP Extract Dilution Buffer, (proprietary).
8.5 ATP Extraction Reagent, (proprietary).
8.6 Luciferin-Luciferase Reagent, (proprietary). Store between –20 °C and 4 °C; allow to equilibrate to ambient temperature
before using.
NOTE 5—Follow manufacturers’ instructions regarding product storage and shelf life.
9. Hazards
9.1 Warning—Not all luminometers are explosion proof. Luminometers that are not explosion-proof should not be operated in
explosive atmospheres or in locations where there may be explosive fumes, as it cannot be grounded. Consult the manufacturer’s
guidelines for further information.
10. Precaution
10.1 This standard may involve the use of hazardous materials, operations, and equipment. It is the responsibility of whoever uses
this standard to establish appropriate safety practices and to determine the applicability of regulatory limitations prior to use.
11. Sample Collection
11.1 The sample sites should correspond as closely as possible to those selected for chemical, biological, and microbiological
sampling, so that there is maximum correlation of results. The sample collection method will be determined by study objectives.
To collect a sample, use a nonmetallic water sampling bottle. Extraction procedures should be performed immediately after
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.
The sole source of supply of the proprietary ATP dilution buffer, ATP extraction reagent, filter wash reagent, and Luciferin-Luciferase reagent, is LuminUltra Technologies
Ltd., Fredericton, New Brunswick, Canada, http://www.luminultra.com. If you are aware of alternative suppliers, please provide this information to ASTM International
Headquarters. Your comments will receive careful consideration at a meeting of the responsible technical committee, which you may attend.
D4012 − 23a
collection. The sample may be stored 2 h to 3 h if necessary if the temperature and lighting conditions are maintained; for example,
do not place a warm sample from a well-lighted area into a cool, dark ice chest.
12. Calibration and Standardization
12.1 It is necessary to perform only one calibration during each set of tests performed on the same day, using the same reagent
batches, under the same temperature, using the same materials and the same luminometer. In general, one calibration per day of
testing is sufficient so long as the aforementioned variables are kept the same.
NOTE 6—Although multi-point calibration is not required, guidance on performing a multi-point calibration is provided in Appendix X2.
12.2 Turn on power to luminometer (6.4) and allow instrument to equilibrate, in accordance with manufacturer’s recommenda-
tions.
12.2.1 It is possible, that during prolonged use, over the course of several hours, some luminometer models will heat up
sufficiently to affect the temperature of the reactants (13.25) to affect the test result (13.25). Excessive on-time can also stimulate
the photomultiplier tube to produce increased instrument background noise. Consequently, it is advisable to repeat 12.6 – 12.9 after
every 3 h of continuous operation.
12.3 Ensure that all reagents have equilibrated to ambient temperature (22 °C 6 3 °C) before running any tests.
NOTE 7—The kinetics of the enzymatic reaction measured by this procedure are affected by temperature.
12.3.1 It is important to ensure that the assay is performed at constant temperature (T 6 3 °C), that is, the instrument and all
reagents must remain at same temperature during the measurement series.
12.3.2 If the measurement results are to be compared to a standard curve or control samples these must be measured at the same
conditions and temperature as the test sample.
12.3.3 Changes in the instrument, diluted sample (13.19) ATP standard (8.3) or Luciferin-Luciferase reagent (8.6) temperature
while testing multiple samples will affect the RLU and consequently introduce a bias to the test results.
12.4 Use a micropipeter (7.6) with a new 100 μL to 1000 μL tip (7.7) to dispense 100 μL Luciferin-Luciferase reagent (8.6) to an
unused 12 mm by 55 mm culture tube (7.1).
12.5 Replace the micropipeter tip with a fresh 100 μL to 1000 μL tip.
12.6 Dispense 100 μL of 1 ng ATP/mL standard solution (8.3) into the culture tube.
12.7 Swirl gently for five times.
12.8 Place the culture tube into the luminometer.
12.9 Read and record RLU (RLU ).
ctrl
13. ATP Measurement Procedure
13.1 Use aseptic procedure while performing this test method; cellular-ATP from analyst’s hands, sputum, etc., can contaminate
the sample with cellular-ATP from sources other than the sample itself.
13.2 Remove plunger from a new 60 mL syringe (7.10) and place onto 17 mm test tube rack so that plunger tip does not contact
any surfaces so as to avoid contamination with ATP.
13.3 Affix filter (7.3) onto the 60 mL syringe.
D4012 − 23a
13.4 Place a fresh 1.0 mL to 5.0 mL tip (7.8) onto the macropipeter (7.5).
13.5 Shake sample for 15 s to ensure homogeneity.
13.6 With minimal delay, remove lid from sample container and, using the macropipeter, transfer ten volumes of 5.0 mL (50 mL
total) water sample, or one to the 60 mL syringe barrel.
13.6.1 If desired, consult Appendix X3 for guidelines on adjusting method detection range by modifying the standard sample
volume.
13.7 While holding the barrel over the waste receptacle (7.13), replace the plunger into the 60 mL syringe.
13.8 Apply even pressure to the 60 mL syringe plunger to pressure filter the sample, having filtrate discharge into the waste
receptacle.
13.8.1 For samples having high particulate loads, it may not be possible to filter the full subsample. When this occurs, record the
actual volume filtered and substitute this value for “V” in Eq 1 (14.1).
13.9 Remove filter from the 60 mL syringe and place onto 17 mm test tube rack (7.12) so that filter outlet does not contact any
surfaces.
13.10 Remove plunger from the 60 mL syringe and place onto 17 mm test tube rack so that plunger tip does not contact any
surfaces so as to avoid contamination with ATP.
13.11 Replace filter onto the end of the 60 mL syringe barrel.
13.12 Place an unused 17 mm by 100 mm culture tube (7.2) into 17 mm test tube rack.
13.13 Place a fresh 100 μL to 1000 μL pipet tip onto the micropipeter.
13.14 Use micropipeter to dispense 1.0 mL of ATP extraction reagent (8.5) into the 60 mL syringe barrel.
13.15 While holding the barrel over the 17 mm by 100 mm culture tube (13.12), replace the 60 mL syringe plunger.
13.16 Apply even pressure to the 60 mL syringe plunger, to dispense ATP Extraction Reagent and extracted ATP into the 17 mm
by 100 mm culture tube.
NOTE 8—At this point in the protocol, this ATP extract may be stored for up to seven days at 2 °C to 8 °C prior to completing the test.
13.17 If not already performed (12.2), turn power on luminometer (7.4) and allow instrument to equilibrate, in accordance with
manufacturer’s recommendations.
13.18 Place a fresh 1.0 mL to 5.0 mL pipet tip onto the macropipeter.
13.19 Use macropipeter to dispense two 4.5 mL portions (9.0 mL total) of ATP extract dilution buffer (8.4) into the culture tube
to prepare diluted ATP extract.
13.20 Place cap on culture tube and invert three times to mix well.
NOTE 9—Diluted ATP extract is stable for up to 4 h at room temperature (20 °C 6 2 °C).
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