ASTM D5176-20
(Test Method)Standard Test Method for Total Chemically Bound Nitrogen in Water by Pyrolysis and Chemiluminescence Detection
Standard Test Method for Total Chemically Bound Nitrogen in Water by Pyrolysis and Chemiluminescence Detection
SIGNIFICANCE AND USE
5.1 This test method is useful for the determination of total chemically bound nitrogen in wastewaters and other waters.
SCOPE
1.1 This test method covers the determination of the total nitrogen content of water in concentrations from 0.5 to 1000 mg/L. Higher nitrogen concentrations may be determined by making the proper dilutions.
1.2 This test method does not determine molecular nitrogen (N2).
1.3 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this 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.
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
- 14-Jul-2020
- Technical Committee
- D19 - Water
- Drafting Committee
- D19.06 - Methods for Analysis for Organic Substances in Water
Relations
- Effective Date
- 01-May-2020
- Effective Date
- 15-Jun-2012
- Effective Date
- 01-Mar-2010
- Effective Date
- 15-Jan-2008
- Effective Date
- 01-Sep-2006
- Effective Date
- 01-Sep-2006
- Effective Date
- 15-Aug-2006
- Effective Date
- 01-Mar-2006
- Effective Date
- 15-Feb-2006
- Effective Date
- 01-Mar-2004
- Effective Date
- 01-Mar-2004
- Effective Date
- 10-Aug-2003
- Effective Date
- 10-Aug-2003
- Effective Date
- 10-Mar-2003
- Effective Date
- 10-Jul-2002
Overview
ASTM D5176-20 is the standard test method for determining total chemically bound nitrogen in water using pyrolysis and chemiluminescence detection. Developed by ASTM International, this standard provides a comprehensive approach to accurately measuring nitrogen concentrations in various water samples, including wastewaters and other environmental or industrial waters. D5176-20 covers nitrogen concentrations from 0.5 to 1000 mg/L, with the ability to assess higher levels through dilution.
This test method does not detect molecular nitrogen (N₂) but rather quantifies all inorganic and organic forms of chemically bound nitrogen. It is an essential tool for laboratories performing water quality analysis and regulatory compliance testing, offering a precise and standardized technique for total nitrogen determination.
Key Topics
- Scope of Measurement: Suitable for total chemically bound nitrogen across a wide concentration range (0.5 - 1000 mg/L).
- Test Method Summary: Utilizes oxidative pyrolysis of the water sample to convert bound nitrogen to nitric oxide (NO), followed by chemiluminescent detection as NO reacts with ozone, emitting detectable light.
- Standards and Precision: Includes requirements for reagents, apparatus, calibration, and quality control procedures to ensure accurate and reproducible results.
- Application Range: Ideal for wastewaters and a variety of other waters where total nitrogen assessment is required.
- Exclusions: Does not determine free molecular nitrogen (N₂) in the sample.
- Safety and Compliance: Users must establish their own safety and environmental practices and be aware of applicable regulatory requirements.
Applications
The ASTM D5176-20 standard is widely adopted in the following areas:
- Water Quality Monitoring: Essential for governmental agencies, environmental laboratories, and wastewater treatment facilities conducting nitrogen assessments for regulatory compliance.
- Industrial Wastewater Testing: Used by industrial plants to monitor and control nitrogen levels in effluents, ensuring adherence to discharge permits.
- Environmental Research: Facilitates scientific studies examining nitrogen pollution, nutrient loading, and ecosystem impacts in rivers, lakes, and coastal waters.
- Quality Control: Laboratories use this method for validation and quality assurance in routine water analysis.
- Support for Regulatory Reporting: Provides data necessary to comply with standards set by environmental authorities at local, national, or international levels.
Related Standards
For comprehensive water analysis and laboratory testing, the following ASTM standards are commonly referenced in conjunction with ASTM D5176-20:
- ASTM D1129: Terminology Relating to Water
- ASTM D1193: Specification for Reagent Water
- ASTM D2777: Practice for Determination of Precision and Bias of Applicable Test Methods of Committee D19 on Water
- ASTM D5847: Practice for Writing Quality Control Specifications for Standard Test Methods for Water Analysis
These related standards support the implementation of robust water testing procedures and help ensure the reliability and accuracy of analytical results.
Keywords: total chemically bound nitrogen, water analysis, chemiluminescence detection, ASTM D5176-20, nitrogen in water, wastewater testing, water quality standard, environmental compliance, pyrolysis, laboratory water testing.
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Frequently Asked Questions
ASTM D5176-20 is a standard published by ASTM International. Its full title is "Standard Test Method for Total Chemically Bound Nitrogen in Water by Pyrolysis and Chemiluminescence Detection". This standard covers: SIGNIFICANCE AND USE 5.1 This test method is useful for the determination of total chemically bound nitrogen in wastewaters and other waters. SCOPE 1.1 This test method covers the determination of the total nitrogen content of water in concentrations from 0.5 to 1000 mg/L. Higher nitrogen concentrations may be determined by making the proper dilutions. 1.2 This test method does not determine molecular nitrogen (N2). 1.3 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this 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. 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 This test method is useful for the determination of total chemically bound nitrogen in wastewaters and other waters. SCOPE 1.1 This test method covers the determination of the total nitrogen content of water in concentrations from 0.5 to 1000 mg/L. Higher nitrogen concentrations may be determined by making the proper dilutions. 1.2 This test method does not determine molecular nitrogen (N2). 1.3 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this 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. 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 D5176-20 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 D5176-20 has the following relationships with other standards: It is inter standard links to ASTM D1129-13(2020)e2, ASTM D2777-12, ASTM D1129-10, ASTM D2777-08, ASTM D1129-06a, ASTM D1129-06ae1, ASTM D2777-06, ASTM D1193-06, ASTM D1129-06, ASTM D1129-04e1, ASTM D1129-04, ASTM D1129-03a, ASTM D2777-03, ASTM D1129-03, ASTM D1129-02a. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.
ASTM D5176-20 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: D5176 − 20
Standard Test Method for
Total Chemically Bound Nitrogen in Water by Pyrolysis and
Chemiluminescence Detection
This standard is issued under the fixed designation D5176; 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 3. Terminology
3.1 Definitions:
1.1 This test method covers the determination of the total
3.1.1 For definitions of terms used in this standard, refer to
nitrogen content of water in concentrations from 0.5 to 1000
Terminology D1129.
mg/L. Higher nitrogen concentrations may be determined by
making the proper dilutions.
3.2 Definitions of Terms Specific to This Standard:
3.2.1 total chemically bound nitrogen, n—all inorganic and
1.2 This test method does not determine molecular nitrogen
organicnitrogeninthesample,exceptmolecularnitrogen(N ).
(N ).
4. Summary of Test Method
1.3 The values stated in SI units are to be regarded as
standard. No other units of measurement are included in this
4.1 The sample of water is introduced into a stream of
standard.
oxygen or inert/oxygen mix flowing through a quartz pyrolysis
tube. Oxidative pyrolysis converts chemically bound nitrogen
1.4 This standard does not purport to address all of the
to nitric oxide (NO). The gas stream is dried and the NO is
safety concerns, if any, associated with its use. It is the
contacted with ozone (O ) producing metastable nitrogen
responsibility of the user of this standard to establish appro-
dioxide (NO *). As the NO * decays, light is emitted and
priate safety, health, and environmental practices and deter- 2 2
detected by a photomultiplier tube. The resulting signal is a
mine the applicability of regulatory limitations prior to use.
measure of the total chemically bound nitrogen in the sample.
1.5 This international standard was developed in accor-
dance with internationally recognized principles on standard-
5. Significance and Use
ization established in the Decision on Principles for the
5.1 This test method is useful for the determination of total
Development of International Standards, Guides and Recom-
chemically bound nitrogen in wastewaters and other waters.
mendations issued by the World Trade Organization Technical
Barriers to Trade (TBT) Committee. 6. Apparatus
6.1 Pyrolysis Furnace—An electric tube furnace capable of
2. Referenced Documents
achieving a temperature of 1100°C. The furnace may be single
or multizoned and may have common or separate and inde-
2.1 ASTM Standards:
pendent temperature controls.
D1129 Terminology Relating to Water
D1193 Specification for Reagent Water
6.2 Pyrolysis Tube—The pyrolysis tube must be fabricated
D2777 Practice for Determination of Precision and Bias of
from quartz and should be designed to ensure complete
Applicable Test Methods of Committee D19 on Water
pyrolysis of a wide variety of samples.
D5847 Practice for Writing Quality Control Specifications
6.3 Chemiluminescence Detector—Thedetectorshallhavea
for Standard Test Methods for Water Analysis
photomultiplier tube capable of sensing the light emission of
the decaying NO *. The detector shall have digital display,
onboard ozone generator and analog output for data system or
This test method is under the jurisdiction of ASTM Committee D19 on Water
strip chart recorder.
andisthedirectresponsibilityofSubcommitteeD19.06onMethodsforAnalysisfor
6.4 Recorder (optional)—The recorder shall be able to
Organic Substances in Water.
Current edition approved July 15, 2020. Published July 2020. Originally
accept a 1 V full scale signal and to provide a chart speed of 1
approved in 1991. Last previous edition approved in 2015 as D5176 – 08 (2015).
cm/min.
DOI: 10.1520/D5176-20.
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 The apparatus described in 6.1 – 6.7 is manufactured by Antek Instruments,
Standards volume information, refer to the standard’s Document Summary page on Inc., Houston, TX, and Dohrmann Division of Rosemount Analytical Inc., Santa
the ASTM website. Clara, CA, and was used in the validation study of this test method.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D5176 − 20
6.5 Microlitre Syringe—Any standard series of microlitre 9.3 Syringe Injection—Fill the syringe to the 5 µLmark and
syringes with stainless steel needles is acceptable. See manu- retract the plunger so that the liquid meniscus is at the 1 µL
facturer’s instructions for appropriate syringe sizes. mark. Note the position of the plunger. Insert the syringe
needle through the inlet septum up to the syringe barrel and
6.6 Syringe Drive Mechanism—The syringe drive shall be
allow the furnace to burn all nitrogen bearing residue off the
capable of driving the sample from a microlitre syringe at a
syringe needle. Reset the detector and inject the sample at a
controlled, reproducible rate.
controlled rate of 1 to 2 µL/s.Asyringe drive mechanism (see
6.7 Sample Boat—Samples with high concentrations of
6.6) is strongly recommended. When all sample has been
suspended matter or dissolved nonvolatile compounds may
injected, withdraw the syringe needle. Retract the plunger so
tendtoplugthesyringeneedleuponinjectionintothepyrolysis
that the sample meniscus is again at the 1 µLpoint and note the
tube. In this case a sample boat of quartz or platinum, with or
plunger position. The true amount injected is the difference
without quartz wool, should be used, in conjunction with the
between the two plunger positions.
appropriate pyrolysis tube. The pyrolysis tube shall allow the
NOTE 1—If water samples contain high concentrations of suspended
introduction of the sample into the boat by microlitre syringe
matter or dissolved nonvolatile compounds, the syringe needle may tend
without interrupting the gas flow system.
to plug or the precision and bias of the test method may be degraded. In
such a case, the sample boat system should be used (see 6.7).
7. Reagents and Materials
9.4 Boat Injection—Fill the microlitre syringe to the mark
7.1 Purity of Reagents—Reagent grade chemicals shall be
and inject the sample directly into the boat while holding the
used.Unlessotherwiseindicated,itisintendedthatallreagents
needle in contact with the side of the boat or with the quartz
shall conform to the specifications of the Committee on
wool.
Analytical Reagents of the American Chemical Society.
9.5 Determine each calibration standard and the zero blank
Other grades may be used, provided it is first determined that
three times and record the net response from the average of
the reagent is of sufficiently high purity to permit its use
each set of standard responses.
without lessening the accuracy of the determination.
9.6 By injecting the same volumetric amount of sample for
7.2 Purity of Water—Unless otherwise indicated, references
each determination, the only variables will be total nitrogen
to water shall be understood to mean reagent water that meets
concentrationanddetectorresponse(digitaldisplay).Construct
the purity specifications of Type I or Type II water, presented
a curve plotting milligrams of N per litre versus detector
in Specification D1193.
response. Check the complete calibration curve at least once
7.3 Inert Gas, Argon (minimum purity 99.99 %).
per week; check one or two standards daily.
7.4 Oxygen (minimum purity 99.6 %).
10. Procedure
7.5 Stock Solution, Pyridine (10 000 mg N/L)—Prepare by
10.1 Flush the microlitre syringe several times with the
accurately weighing 5.647 g of pyridine into a 100 mL
unknown sample. Inject the sample at a controlled rate of 1 to
volumetric flask and dilute to 100 mL with water.
2 µg/s as described in 9.3 or inject the sample into the sample
7.6 Pyridine Solutions, Standard (1000, 500, 100, 50, 10, 5,
boat (see 6.7) as described in 9.4.
1, and 0.5 mg N/L)—Dilute ten volumes of the stock solution
10.2 Set instrument parameters as recommende
...
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: D5176 − 08 (Reapproved 2015) D5176 − 20
Standard Test Method for
Total Chemically Bound Nitrogen in Water by Pyrolysis and
Chemiluminescence Detection
This standard is issued under the fixed designation D5176; 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 the determination of the total nitrogen content of water in concentrations from 0.5 to 1000 mg/L.
Higher nitrogen concentrations may be determined by making the proper dilutions.
1.2 This test method does not determine molecular nitrogen (N ).
1.3 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this 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 safety, health, and healthenvironmental practices and determine the
applicability of regulatory limitations prior to use.
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
D2777 Practice for Determination of Precision and Bias of Applicable Test Methods of Committee D19 on Water
D5847 Practice for Writing Quality Control Specifications for Standard Test Methods for Water Analysis
3. Terminology
3.1 Definitions:
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 total chemically bound nitrogen, n—all inorganic and organic nitrogen in the sample, except molecular nitrogen (N ).
4. Summary of Test Method
4.1 The sample of water is introduced into a stream of oxygen or inert/oxygen mix flowing through a quartz pyrolysis tube.
Oxidative pyrolysis converts chemically bound nitrogen to nitric oxide (NO). The gas stream is dried and the NO is contacted with
ozone (O ) producing metastable nitrogen dioxide (NO *). As the NO * decays, light is emitted and detected by a photomultiplier
3 2 2
tube. The resulting signal is a measure of the total chemically bound nitrogen in the sample.
5. Significance and Use
5.1 This test method is useful for the determination of total chemically bound nitrogen in wastewaters and other waters.
This test method is under the jurisdiction of ASTM Committee D19 on Water and is the direct responsibility of Subcommittee D19.06 on Methods for Analysis for
Organic Substances in Water.
Current edition approved June 15, 2015July 15, 2020. Published June 2015July 2020. Originally approved in 1991. Last previous edition approved in 20082015 as
D5176 – 08.D5176 – 08 (2015). DOI: 10.1520/D5176-08R15.10.1520/D5176-20.
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’sstandard’s Document Summary page on the ASTM website.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D5176 − 20
6. Apparatus
6.1 Pyrolysis Furnace—An electric tube furnace capable of achieving a temperature of 1100°C. The furnace may be single or
multizoned and may have common or separate and independent temperature controls.
6.2 Pyrolysis Tube—The pyrolysis tube must be fabricated from quartz and should be designed to ensure complete pyrolysis of
a wide variety of samples.
6.3 Chemiluminescence Detector—The detector shall have a photomultiplier tube capable of sensing the light emission of the
decaying NO *. The detector shall have digital display, onboard ozone generator and analog output for data system or strip chart
recorder.
6.4 Recorder (optional)—The recorder shall be able to accept a 1 V full scale signal and to provide a chart speed of 1 cm/min.
6.5 Microlitre Syringe—Any standard series of microlitre syringes with stainless steel needles is acceptable. See
manufacturer’smanufacturer’s instructions for appropriate syringe sizes.
6.6 Syringe Drive Mechanism—The syringe drive shall be capable of driving the sample from a microlitre syringe at a
controlled, reproducible rate.
6.7 Sample Boat—Samples with high concentrations of suspended matter or dissolved nonvolatile compounds may tend to plug
the syringe needle upon injection into the pyrolysis tube. In this case a sample boat of quartz or platinum, with or without quartz
wool, should be used, in conjunction with the appropriate pyrolysis tube. The pyrolysis tube shall allow the introduction of the
sample into the boat by microlitre syringe without interrupting the gas flow system.
7. Reagents and Materials
7.1 Purity of Reagents—Reagent grade chemicals shall be used. 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. Other grades may be
used, provided it is first determined that the reagent is of sufficiently high purity to permit its use without lessening the accuracy
of the determination.
7.2 Purity of Water—Unless otherwise indicated, references to water shall be understood to mean reagent water that meets the
purity specifications of Type I or Type II water, presented in Specification D1193.
7.3 Inert Gas, Argon (minimum purity 99.99 %).
7.4 Oxygen (minimum purity 99.6 %).
7.5 Stock Solution, Pyridine (10 000 mg N/L)—Prepare by accurately weighing 5.647 g of pyridine into a 100 mL volumetric
flask and dilute to 100 mL with water.
7.6 Pyridine Solutions, Standard (1000, 500, 100, 50, 10, 5, 1, and 0.5 mg N/L)—Dilute ten volumes of the stock solution (see
6.5) with 90 volumes of water to prepare a 1000 mg N/L standard. Similarly, by serial dilution with water, prepare 500, 100, 50,
10, 5, 1, and 0.5 mg N/L standards.
8. Preparation of Apparatus
8.1 Assemble apparatus according to manufacturer’smanufacturer’s instructions.
9. Calibration and Standardization
9.1 Use the water that was used to prepare the standards as a zero blank standard.
9.2 A sample size of 5 to 10 μL is sufficient to cover the concentration range of this test method. The volume of the sample shall
be accurately determined.
9.3 Syringe Injection—Fill the syringe to the 5 μL mark and retract the plunger so that the liquid meniscus is at the 1 μL mark.
Note the position of the plunger. Insert the syringe needle through the inlet septum up to the syringe barrel and allow the furnace
to burn all nitrogen bearing residue off the syringe needle. Reset the detector and inject the sample at a controlled rate of 1 to 2
μL/s. A syringe drive mechanism (see 6.6) is strongly recommended. When all sample has been injected, withdraw the syringe
needle. Retract the plunger so that the sample meniscus is again at the 1 μL point and note the plunger position. The true amount
injected is the difference between the two plunger positions.
NOTE 1—If water samples contain high concentrations of suspended matter or dissolved nonvolatile compounds, the syringe needle may tend to plug
The apparatus described in 6.1 – 6.7 is manufactured by Antek Instruments, Inc., Houston, TX, and Dohrmann Division of Rosemount Analytical Inc., Santa Clara, CA,
and was used in the validation study of this test method.
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. PharmaceuticalPharmacopeial Convention, Inc.
(USPC), Rockville, MD.
D5176 − 20
or the precision and bias of the test method
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