Standard Test Methods for Chemical Analysis of Tool Steels and Other Similar Medium- and High-Alloy Steels

SIGNIFICANCE AND USE
4.1 These test methods for the chemical analysis of metals and alloys are primarily intended as referee methods to test such materials for compliance with compositional specifications particularly those under the jurisdiction of ASTM Committee A01 on Steel, Stainless Steel, and Related Alloys. It is assumed that all who use these test methods will be trained analysts capable of performing common laboratory procedures skillfully and safely. It is expected that work will be performed in a properly equipped laboratory under appropriate quality control practices such as those described in Guide E882.
SCOPE
1.1 These test methods cover the chemical analysis of tool steels and other similar medium- and high-alloy steels having chemical compositions within the following limits:    
Element  
Composition Range, %  
Aluminum  
0.005 to 1.5  
Boron  
0.001 to 0.10  
Carbon  
0.03 to 2.50  
Chromium  
0.10 to 14.0  
Cobalt  
0.10 to 14.0  
Copper  
0.01 to 2.0  
Lead  
0.001 to 0.01  
Manganese  
0.10 to 15.00  
Molybdenum  
0.01 to 10.00  
Nickel  
0.02 to 4.00  
Nitrogen  
0.001 to 0.20  
Phosphorus  
0.002 to 0.05  
Silicon  
0.10 to 2.50  
Sulfur  
0.002 to 0.40  
Tungsten  
0.01 to 21.00  
Vanadium  
0.02 to 5.50  
1.2 The test methods in this standard are contained in the sections indicated below:    
Sections  
Carbon, Total, by the Combustion—
Thermal Conductivity Method—
Discontinued 1986  
125–135  
Carbon, Total, by the Combustion Gravimetric
Method—Discontinued 2012  
78–88  
Chromium by the Atomic Absorption
Spectrometry Method  
(0.006 % to 1.00 %)  
174–183  
Chromium by the Peroxydisulfate
Oxidation—Titration Method  
(0.10 % to 14.00 %)  
184–192  
Chromium by the Peroxydisulfate-Oxidation
Titrimetric Method—Discontinued 1980  
117–124  
Cobalt by the Ion-Exchange—
Potentiometric Titration Method  
(2 % to 14 %)  
52–59  
Cobalt by the Nitroso-R-Salt
Spectrophotometric Method  
(0.10 % to 5.0 %)  
60–69  
Copper by the Neocuproine
Spectrophotometric Method  
(0.01 % to 2.00 %)  
89–98  
Copper by the Sulfide Precipitation-
Electrodeposition Gravimetric Method  
(0.01 % to 2.0 %)  
70–77  
Lead by the Ion-Exchange—Atomic
Absorption Spectrometry Method  
(0.001 % to 0.01 %)  
99–108  
Manganese by the Periodate
Spectrophotometric Method  
(0.10 % to 5.00 %)  
9–18  
Molybdenum by the Ion Exchange–
8-Hydroxyquinoline Gravimetric Method  
203–210  
Molybdenum by the Thiocyanate Spectrophotometric Method  
(0.01 % to 1.50 %)  
162–173  
Nickel by the Dimethylglyoxime
Gravimetric Method  
(0.1 % to 4.0 %)  
144–151  
Phosphorus by the Alkalimetric Method  
(0.01 % to 0.05 %)  
136–143  
Phosphorus by the Molybdenum Blue
Spectrophotometric Method  
(0.002 % to 0.05 %)  
19–29  
Silicon by the Gravimetric Method  
(0.10 % to 2.50 %)  
45–51  
Sulfur by the Gravimetric
Method—Discontinued 1988  
29–35  
Sulfur by the Combustion-Iodate
Titration Method—Discontinued 2012  
36–44  
Sulfur by the Chromatographic
Gravimetric Method—Discontinued 1980  
109–116  
Tin by the Solvent Extraction—
Atomic Absorption Spectrometry Method  
(0.002 % to 0.10 %)  
152–161  
Vanadium by the Atomic
Absorption Spectrometry Method  
(0.006 % to 0.15 %)  
193–202  
1.3 Test methods for the determination of carbon and sulfur not included in this standard can be found in Test Methods E1019.  
1.4 Some of the composition ranges given in 1.1 are too broad to be covered by a single test method and therefore this standard contains multiple test methods for some elements. The user must select the proper test method by matching the information given in the Scope and Interference sections of each test method with the composition of the alloy to be analy...

General Information

Status
Published
Publication Date
14-Nov-2023

Relations

Effective Date
15-Nov-2023
Effective Date
15-Nov-2023
Effective Date
15-Mar-2018
Effective Date
15-Nov-2023
Effective Date
15-Nov-2023
Effective Date
15-Nov-2023
Effective Date
15-Nov-2023
Effective Date
15-Nov-2023
Effective Date
15-Nov-2023

Overview

ASTM E352-23: Standard Test Methods for Chemical Analysis of Tool Steels and Other Similar Medium- and High-Alloy Steels is a crucial standard developed by ASTM International for laboratories and quality assurance professionals. This standard specifies referee methods for determining chemical composition in tool steels, as well as related medium- and high-alloy steels. The procedures ensure accurate assessment of key alloying elements within defined composition ranges-supporting compliance with compositional specifications, particularly those overseen by ASTM Committee A01 on Steel, Stainless Steel, and Related Alloys.

Key Topics

  • Purpose and Scope

    • Provides standardized referee test methods for compliance assessment of tool steels and similar alloys.
    • Covers a wide range of key elements including aluminum, boron, carbon, chromium, cobalt, copper, lead, manganese, molybdenum, nickel, nitrogen, phosphorus, silicon, sulfur, tungsten, and vanadium.
    • Designed for trained analysts in well-equipped laboratories who follow established quality control guidelines.
  • Test Methods

    • Methods include atomic absorption spectrometry, spectrophotometry, gravimetric analysis, and titration.
    • Multiple test methods for a given element may be provided due to wide composition ranges.
    • Selection of the appropriate method depends on the chemical composition of the sample and specific requirements detailed in each method.
    • For elements such as carbon and sulfur not covered in this document, referenced methods are provided in ASTM E1019.
  • Quality Control & Safety

    • Emphasizes the importance of laboratory safety, proper apparatus, and reagent purity.
    • Adheres to internationally recognized principles and quality practices, including those described in Guide E882.
    • Laboratories must ensure compliance with safety, health, and environmental requirements before conducting tests.

Applications

ASTM E352-23 is widely applied in:

  • Quality Control: Ensuring raw materials and finished products meet material composition specifications for tool steels and high-alloyed steels.
  • Referee Laboratory Analysis: Serving as the final authority in case of disputes or for verification during audits and certification.
  • Research and Development: Supporting alloy design and performance studies where accurate chemical analysis is essential.
  • Production and Process Control: Helping steel producers, fabricators, and end-users monitor alloy consistency, reduce defects, and optimize heat treatment processes.

The test methods covered are applicable in industries producing or utilizing tool steels, high-speed steels, die steels, and other medium- or high-alloy grades for critical, high-stress applications.

Related Standards

To enhance or supplement the practices outlined in ASTM E352-23, the following standards provide additional guidance:

  • ASTM E29 - Practice for Using Significant Digits in Test Data to Determine Conformance with Specifications
  • ASTM E50 - Practices for Apparatus, Reagents, and Safety in Chemical Analysis of Metals
  • ASTM E60 - Practice for Analysis of Metals, Ores, and Related Materials by Spectrophotometry
  • ASTM E1019 - Test Methods for Determination of Carbon, Sulfur, Nitrogen, and Oxygen in Metals
  • ASTM E882 - Guide for Accountability and Quality Control in the Chemical Analysis Laboratory
  • ASTM E351 - Test Methods for Chemical Analysis of Cast Iron
  • ASTM E353 - Test Methods for Chemical Analysis of Stainless, Heat-Resisting, and Maraging Alloys
  • ISO 5725 - Precision of Test Methods - Determination of Repeatability and Reproducibility

Summary

ASTM E352-23 is essential for accurate, reliable chemical analysis of tool steels and similar alloys, providing confidence in material performance and compliance. Its referee test methods support industry-wide consistency, product certification, and the integrity of both production and research activities.

Keywords: ASTM E352, chemical analysis, tool steels, alloy steels, spectrophotometry, referee methods, laboratory standards, quality control, steel composition testing, metallurgical analysis.

Buy Documents

Standard

ASTM E352-23 - Standard Test Methods for Chemical Analysis of Tool Steels and Other Similar Medium- and High-Alloy Steels

English language (38 pages)
sale 15% off
sale 15% off
Standard

REDLINE ASTM E352-23 - Standard Test Methods for Chemical Analysis of Tool Steels and Other Similar Medium- and High-Alloy Steels

English language (38 pages)
sale 15% off
sale 15% off

Get Certified

Connect with accredited certification bodies for this standard

Element Materials Technology

Materials testing and product certification.

UKAS United Kingdom Verified

Inštitut za kovinske materiale in tehnologije

Institute of Metals and Technology. Materials testing, metallurgical analysis, NDT.

SA Slovenia Verified

Sponsored listings

Frequently Asked Questions

ASTM E352-23 is a standard published by ASTM International. Its full title is "Standard Test Methods for Chemical Analysis of Tool Steels and Other Similar Medium- and High-Alloy Steels". This standard covers: SIGNIFICANCE AND USE 4.1 These test methods for the chemical analysis of metals and alloys are primarily intended as referee methods to test such materials for compliance with compositional specifications particularly those under the jurisdiction of ASTM Committee A01 on Steel, Stainless Steel, and Related Alloys. It is assumed that all who use these test methods will be trained analysts capable of performing common laboratory procedures skillfully and safely. It is expected that work will be performed in a properly equipped laboratory under appropriate quality control practices such as those described in Guide E882. SCOPE 1.1 These test methods cover the chemical analysis of tool steels and other similar medium- and high-alloy steels having chemical compositions within the following limits: Element Composition Range, % Aluminum 0.005 to 1.5 Boron 0.001 to 0.10 Carbon 0.03 to 2.50 Chromium 0.10 to 14.0 Cobalt 0.10 to 14.0 Copper 0.01 to 2.0 Lead 0.001 to 0.01 Manganese 0.10 to 15.00 Molybdenum 0.01 to 10.00 Nickel 0.02 to 4.00 Nitrogen 0.001 to 0.20 Phosphorus 0.002 to 0.05 Silicon 0.10 to 2.50 Sulfur 0.002 to 0.40 Tungsten 0.01 to 21.00 Vanadium 0.02 to 5.50 1.2 The test methods in this standard are contained in the sections indicated below: Sections Carbon, Total, by the Combustion— Thermal Conductivity Method— Discontinued 1986 125–135 Carbon, Total, by the Combustion Gravimetric Method—Discontinued 2012 78–88 Chromium by the Atomic Absorption Spectrometry Method (0.006 % to 1.00 %) 174–183 Chromium by the Peroxydisulfate Oxidation—Titration Method (0.10 % to 14.00 %) 184–192 Chromium by the Peroxydisulfate-Oxidation Titrimetric Method—Discontinued 1980 117–124 Cobalt by the Ion-Exchange— Potentiometric Titration Method (2 % to 14 %) 52–59 Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.10 % to 5.0 %) 60–69 Copper by the Neocuproine Spectrophotometric Method (0.01 % to 2.00 %) 89–98 Copper by the Sulfide Precipitation- Electrodeposition Gravimetric Method (0.01 % to 2.0 %) 70–77 Lead by the Ion-Exchange—Atomic Absorption Spectrometry Method (0.001 % to 0.01 %) 99–108 Manganese by the Periodate Spectrophotometric Method (0.10 % to 5.00 %) 9–18 Molybdenum by the Ion Exchange– 8-Hydroxyquinoline Gravimetric Method 203–210 Molybdenum by the Thiocyanate Spectrophotometric Method (0.01 % to 1.50 %) 162–173 Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 4.0 %) 144–151 Phosphorus by the Alkalimetric Method (0.01 % to 0.05 %) 136–143 Phosphorus by the Molybdenum Blue Spectrophotometric Method (0.002 % to 0.05 %) 19–29 Silicon by the Gravimetric Method (0.10 % to 2.50 %) 45–51 Sulfur by the Gravimetric Method—Discontinued 1988 29–35 Sulfur by the Combustion-Iodate Titration Method—Discontinued 2012 36–44 Sulfur by the Chromatographic Gravimetric Method—Discontinued 1980 109–116 Tin by the Solvent Extraction— Atomic Absorption Spectrometry Method (0.002 % to 0.10 %) 152–161 Vanadium by the Atomic Absorption Spectrometry Method (0.006 % to 0.15 %) 193–202 1.3 Test methods for the determination of carbon and sulfur not included in this standard can be found in Test Methods E1019. 1.4 Some of the composition ranges given in 1.1 are too broad to be covered by a single test method and therefore this standard contains multiple test methods for some elements. The user must select the proper test method by matching the information given in the Scope and Interference sections of each test method with the composition of the alloy to be analy...

SIGNIFICANCE AND USE 4.1 These test methods for the chemical analysis of metals and alloys are primarily intended as referee methods to test such materials for compliance with compositional specifications particularly those under the jurisdiction of ASTM Committee A01 on Steel, Stainless Steel, and Related Alloys. It is assumed that all who use these test methods will be trained analysts capable of performing common laboratory procedures skillfully and safely. It is expected that work will be performed in a properly equipped laboratory under appropriate quality control practices such as those described in Guide E882. SCOPE 1.1 These test methods cover the chemical analysis of tool steels and other similar medium- and high-alloy steels having chemical compositions within the following limits: Element Composition Range, % Aluminum 0.005 to 1.5 Boron 0.001 to 0.10 Carbon 0.03 to 2.50 Chromium 0.10 to 14.0 Cobalt 0.10 to 14.0 Copper 0.01 to 2.0 Lead 0.001 to 0.01 Manganese 0.10 to 15.00 Molybdenum 0.01 to 10.00 Nickel 0.02 to 4.00 Nitrogen 0.001 to 0.20 Phosphorus 0.002 to 0.05 Silicon 0.10 to 2.50 Sulfur 0.002 to 0.40 Tungsten 0.01 to 21.00 Vanadium 0.02 to 5.50 1.2 The test methods in this standard are contained in the sections indicated below: Sections Carbon, Total, by the Combustion— Thermal Conductivity Method— Discontinued 1986 125–135 Carbon, Total, by the Combustion Gravimetric Method—Discontinued 2012 78–88 Chromium by the Atomic Absorption Spectrometry Method (0.006 % to 1.00 %) 174–183 Chromium by the Peroxydisulfate Oxidation—Titration Method (0.10 % to 14.00 %) 184–192 Chromium by the Peroxydisulfate-Oxidation Titrimetric Method—Discontinued 1980 117–124 Cobalt by the Ion-Exchange— Potentiometric Titration Method (2 % to 14 %) 52–59 Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.10 % to 5.0 %) 60–69 Copper by the Neocuproine Spectrophotometric Method (0.01 % to 2.00 %) 89–98 Copper by the Sulfide Precipitation- Electrodeposition Gravimetric Method (0.01 % to 2.0 %) 70–77 Lead by the Ion-Exchange—Atomic Absorption Spectrometry Method (0.001 % to 0.01 %) 99–108 Manganese by the Periodate Spectrophotometric Method (0.10 % to 5.00 %) 9–18 Molybdenum by the Ion Exchange– 8-Hydroxyquinoline Gravimetric Method 203–210 Molybdenum by the Thiocyanate Spectrophotometric Method (0.01 % to 1.50 %) 162–173 Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 4.0 %) 144–151 Phosphorus by the Alkalimetric Method (0.01 % to 0.05 %) 136–143 Phosphorus by the Molybdenum Blue Spectrophotometric Method (0.002 % to 0.05 %) 19–29 Silicon by the Gravimetric Method (0.10 % to 2.50 %) 45–51 Sulfur by the Gravimetric Method—Discontinued 1988 29–35 Sulfur by the Combustion-Iodate Titration Method—Discontinued 2012 36–44 Sulfur by the Chromatographic Gravimetric Method—Discontinued 1980 109–116 Tin by the Solvent Extraction— Atomic Absorption Spectrometry Method (0.002 % to 0.10 %) 152–161 Vanadium by the Atomic Absorption Spectrometry Method (0.006 % to 0.15 %) 193–202 1.3 Test methods for the determination of carbon and sulfur not included in this standard can be found in Test Methods E1019. 1.4 Some of the composition ranges given in 1.1 are too broad to be covered by a single test method and therefore this standard contains multiple test methods for some elements. The user must select the proper test method by matching the information given in the Scope and Interference sections of each test method with the composition of the alloy to be analy...

ASTM E352-23 is classified under the following ICS (International Classification for Standards) categories: 77.040.30 - Chemical analysis of metals. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM E352-23 has the following relationships with other standards: It is inter standard links to ASTM E352-18e1, ASTM E350-23, ASTM E350-18, ASTM E353-19e1, ASTM A751-21, ASTM E351-18, ASTM E354-21e1, ASTM B733-22, ASTM E1473-22. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM E352-23 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: E352 − 23
Standard Test Methods for
Chemical Analysis of Tool Steels and Other Similar Medium-
and High-Alloy Steels
This standard is issued under the fixed designation E352; 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
Sections
Copper by the Sulfide Precipitation-
1.1 These test methods cover the chemical analysis of tool
Electrodeposition Gravimetric Method (0.01 % to 2.0 %) 70–77
steels and other similar medium- and high-alloy steels having Lead by the Ion-Exchange—Atomic
Absorption Spectrometry Method (0.001 % to 0.01 %) 99–108
chemical compositions within the following limits:
Manganese by the Periodate
Element Composition Range, % Spectrophotometric Method (0.10 % to 5.00 %) 9–18
Aluminum 0.005 to 1.5
Molybdenum by the Ion Exchange–
Boron 0.001 to 0.10 8-Hydroxyquinoline Gravimetric Method 203–210
Carbon 0.03 to 2.50 Molybdenum by the Thiocyanate
Chromium 0.10 to 14.0 Spectrophotometric Method (0.01 % to 1.50 %) 162–173
Cobalt 0.10 to 14.0 Nickel by the Dimethylglyoxime
Copper 0.01 to 2.0 Gravimetric Method (0.1 % to 4.0 %) 144–151
Lead 0.001 to 0.01 Phosphorus by the Alkalimetric Method (0.01 % to 0.05 %) 136–143
Manganese 0.10 to 15.00 Phosphorus by the Molybdenum Blue
Molybdenum 0.01 to 10.00 Spectrophotometric Method (0.002 % to 0.05 %) 19–29
Nickel 0.02 to 4.00 Silicon by the Gravimetric Method (0.10 % to 2.50 %) 45–51
Nitrogen 0.001 to 0.20 Sulfur by the Gravimetric
Method—Discontinued 1988 29–35
Phosphorus 0.002 to 0.05
Silicon 0.10 to 2.50 Sulfur by the Combustion-Iodate
Titration Method—Discontinued 2012 36–44
Sulfur 0.002 to 0.40
Tungsten 0.01 to 21.00 Sulfur by the Chromatographic
Vanadium 0.02 to 5.50 Gravimetric Method—Discontinued 1980 109–116
Tin by the Solvent Extraction—
1.2 The test methods in this standard are contained in the
Atomic Absorption Spectrometry Method (0.002 % to 0.10 %) 152–161
sections indicated below: Vanadium by the Atomic
Absorption Spectrometry Method (0.006 % to 0.15 %) 193–202
Sections
Carbon, Total, by the Combustion— 1.3 Test methods for the determination of carbon and sulfur
Thermal Conductivity Method—
not included in this standard can be found in Test Methods
Discontinued 1986 125–135
E1019.
Carbon, Total, by the Combustion Gravimetric
Method—Discontinued 2012 78–88
1.4 Some of the composition ranges given in 1.1 are too
Chromium by the Atomic Absorption
broad to be covered by a single test method and therefore this
Spectrometry Method (0.006 % to 1.00 %) 174–183
Chromium by the Peroxydisulfate
standard contains multiple test methods for some elements.
Oxidation—Titration Method (0.10 % to 14.00 %) 184–192
The user must select the proper test method by matching the
Chromium by the Peroxydisulfate-Oxidation
Titrimetric Method—Discontinued 1980 117–124 information given in the Scope and Interference sections of
Cobalt by the Ion-Exchange—
each test method with the composition of the alloy to be
Potentiometric Titration Method (2 % to 14 %) 52–59
analyzed.
Cobalt by the Nitroso-R-Salt
Spectrophotometric Method (0.10 % to 5.0 %) 60–69
1.5 The values stated in SI units are to be regarded as
Copper by the Neocuproine
standard.
Spectrophotometric Method (0.01 % to 2.00 %) 89–98
1.6 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 appro-
These test methods are under the jurisdiction of the ASTM Committee E01 on
Analytical Chemistry for Metals, Ores, and Related Materials and are the direct
priate safety, health, and environmental practices and deter-
responsibility of Subcommittee E01.01 on Iron, Steel, and Ferroalloys.
mine the applicability of regulatory limitations prior to use.
Current edition approved Nov. 15, 2023. Published December 2023. Originally
ɛ1 Specific hazards statements are given in Section 6 and in
approved in 1968. Last previous edition approved in 2018 as E352 – 18 . DOI:
10.1520/E0352-23. special “Warning” paragraphs throughout these test methods.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E352 − 23
1.7 This international standard was developed in accor- 3. Terminology
dance with internationally recognized principles on standard-
3.1 For definitions of terms used in these test methods, refer
ization established in the Decision on Principles for the
to Terminology E135.
Development of International Standards, Guides and Recom-
mendations issued by the World Trade Organization Technical
4. Significance and Use
Barriers to Trade (TBT) Committee.
4.1 These test methods for the chemical analysis of metals
and alloys are primarily intended as referee methods to test
2. Referenced Documents
such materials for compliance with compositional specifica-
2.1 ASTM Standards:
tions particularly those under the jurisdiction of ASTM Com-
D1193 Specification for Reagent Water
mittee A01 on Steel, Stainless Steel, and Related Alloys. It is
E29 Practice for Using Significant Digits in Test Data to
assumed that all who use these test methods will be trained
Determine Conformance with Specifications
analysts capable of performing common laboratory procedures
E50 Practices for Apparatus, Reagents, and Safety Consid-
skillfully and safely. It is expected that work will be performed
erations for Chemical Analysis of Metals, Ores, and
in a properly equipped laboratory under appropriate quality
Related Materials
control practices such as those described in Guide E882.
E60 Practice for Analysis of Metals, Ores, and Related
5. Apparatus, Reagents, and Instrumental Practices
Materials by Spectrophotometry
E135 Terminology Relating to Analytical Chemistry for
5.1 Apparatus—Specialized apparatus requirements are
Metals, Ores, and Related Materials
listed in the “Apparatus” Section in each method.
E173 Practice for Conducting Interlaboratory Studies of
5.1.1 In the methods specifying spectrophotometric testing,
Methods for Chemical Analysis of Metals (Withdrawn
the cells utilized to contain the reference material solutions and
1997)
sample solutions in spectrophotometers are referred to as
E350 Test Methods for Chemical Analysis of Carbon Steel,
“absorption cells”. Please note that the radiant energy passed
Low-Alloy Steel, Silicon Electrical Steel, Ingot Iron, and
through the cells can be measured as absorbance or transmit-
Wrought Iron
tance. These methods refer to absorbance measurements. Refer
E351 Test Methods for Chemical Analysis of Cast Iron—All
to Practices E60 for details.
Types
5.2 Reagents:
E353 Test Methods for Chemical Analysis of Stainless,
5.2.1 Purity of Reagents—Reagent grade chemicals shall be
Heat-Resisting, Maraging, and Other Similar Chromium-
used in all tests. Unless otherwise indicated, all reagents shall
Nickel-Iron Alloys
conform to the Specifications of the Committee on Analytical
E354 Test Methods for Chemical Analysis of High-
Reagents of the American Chemical Society where such
Temperature, Electrical, Magnetic, and Other Similar Iron,
specifications are available. Other chemicals may be used,
Nickel, and Cobalt Alloys
provided it is first ascertained that they are of sufficiently high
E882 Guide for Accountability and Quality Control in the
purity to permit their use without adversely affecting the
Chemical Analysis Laboratory
expected performance of the determination, as indicated in the
E1019 Test Methods for Determination of Carbon, Sulfur,
section on “Precision and Bias.”
Nitrogen, and Oxygen in Steel, Iron, Nickel, and Cobalt
5.2.2 Purity of Water—Unless otherwise indicated, refer-
Alloys by Various Combustion and Inert Gas Fusion
ences to water shall mean reagent water conforming to Type I
Techniques
or Type II of Specification D1193. Type III or IV may be used
E1024 Guide for Chemical Analysis of Metals and Metal
if they effect no measurable change in the blank or sample.
Bearing Ores by Flame Atomic Absorption Spectropho-
tometry (Withdrawn 2004) 5.3 Spectrophotometric Practice—Spectrophotometric
practice prescribed in these test methods shall conform to
E1601 Practice for Conducting an Interlaboratory Study to
Evaluate the Performance of an Analytical Method Practice E60.
E1806 Practice for Sampling Steel and Iron for Determina-
6. Hazards
tion of Chemical Composition
6.1 For precautions to be observed in the use of certain
2.2 Other Document:
reagents and equipment in these methods, refer to Practices
ISO 5725 Precision of Test Methods—Determination of
E50.
Repeatability and Reproducibility for Inter-Laboratory
Tests
7. Sampling
7.1 For procedures to sample the material, refer to Practice
E1806.
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. “Reagent Chemicals, American Chemical Society Specifications,” American
The last approved version of this historical standard is referenced on Chemical Society, Washington, DC, www.acs.org. For suggestions on the testing of
www.astm.org. Reagents not listed by the American Chemical Society, see the United States
Available from American National Standards Institute (ANSI), 25 W. 43rd St., Pharmacopeia and National Formulary, U.S. Pharmacopeial Convention, Inc.
4th Floor, New York, NY 10036, http://www.ansi.org. (USPC), Rockville, MD, www.usp.org.
E352 − 23
8. Interlaboratory Studies and Rounding Calculated 13.2 The spectral transmittance curve of permanganate ions
Values exhibits two useful minima, one at approximately 526 nm, and
the other at 545 nm. The latter is recommended when a
8.1 These test methods have been evaluated in accordance
“narrow-band” spectrophotometer is used.
with Practice E173 (withdrawn 1997) or ISO 5725. Practice
E173 has been replaced by Practice E1601. The 13.3 Tungsten, when present in amounts of more than 0.5 %
Reproducibility, R2, of E173 corresponds to the Reproducibil- interferes by producing a turbidity in the final solution. A
ity Index, R, of E1601. The Repeatability, R1, of E173 special procedure is provided for use with samples containing
corresponds to the Repeatability Index, r, of E1601. more than 0.5 % tungsten which eliminates the problem by
preventing the precipitation of the tungsten.
8.2 Rounding of test results obtained using these test meth-
ods shall be performed as directed in ASTM E29, Rounding
14. Reagents
Method, unless an alternative rounding method is specified by
14.1 Manganese, Standard Solution (1 mL = 0.032 mg
the customer or applicable material specification.
Mn)—Transfer the equivalent of 0.4000 g of assayed, high-
purity manganese (purity: 99.99 % minimum), to a 500-mL
MANGANESE BY THE METAPERIODATE
volumetric flask and dissolve in 20 mL of HNO by heating.
SPECTROPHOTOMETRIC METHOD
Cool, dilute to volume, and mix. Using a pipet, transfer 20 mL
to a 500-mL volumetric flask, dilute to volume, and mix.
9. Scope
14.2 Nitric-Phosphoric Acid Mixture—Cautiously, while
9.1 This method covers the determination of manganese
stirring, add 100 mL of HNO and 400 mL of H PO to 400
3 3 4
from 0.10 % to 5.00 %.
mL of water. Cool, dilute to 1 L, and mix. Prepare fresh as
needed.
10. Summary of Method
14.3 Potassium Metaperiodate Solution (7.5 g/L)—Dissolve
10.1 Manganous ions are oxidized to permanganate ions by
7.5 g of potassium metaperiodate (KIO ) in 200 mL of hot
treatment with periodate. Tungsten when present at composi-
HNO (1 + 1), add 400 mL of H PO , cool, dilute to 1 L, and
3 3 4
tions greater than 0.5 % is kept in solution with phosphoric
mix.
acid. Solutions of the samples are fumed with HClO so that
14.4 Water, Pretreated with Metaperiodate—Add 20 mL of
the effect of periodate is limited to the oxidation of manganese.
Spectrophotometric absorbance measurement is made at 545 KIO solution to 1 L of water, mix, heat at not less than 90 °C
for 20 min to 30 min, and cool. Use this water to dilute
nm.
solutions to volume that have been treated with KIO solution
11. Concentration Range
to oxidize manganese, and thus avoid reduction of permangan-
ate ions by any reducing agents in the untreated water.
11.1 The recommended concentration range is 0.15 mg to
(Caution—Avoid the use of this water for other purposes.)
0.8 mg of manganese per 50 mL of solution, using a 1-cm cell
(Note 1) and a spectrophotometer with a band width of 10 nm
15. Preparation of Calibration Curve
or less.
15.1 Calibration Solutions—Using pipets, transfer 5 mL, 10
NOTE 1—This method has been written for cells having a 1-cm light
mL, 15 mL, 20 mL, and 25 mL of manganese standard solution
path and a “narrow-band” instrument. The concentration range depends
(1 mL = 0.032 mg Mn) to 50-mL borosilicate glass volumetric
upon band width and spectral region used as well as cell optical path
length. Cells having other dimensions may be used, provided suitable
flasks, and, if necessary, dilute to approximately 25 mL.
adjustments can be made in the amounts of sample and reagents used.
Proceed as directed in 15.3.
15.2 Reference Solution—Transfer approximately 25 mL of
12. Stability of Color
water to a 50-mL borosilicate glass volumetric flask. Proceed
12.1 The color is stable for at least 24 h.
as directed in 15.3.
13. Interferences 15.3 Color Development—Add 10 mL of KIO solution,
and heat the solutions at not less than 90 °C for 20 min to 30
13.1 HClO treatment, which is used in the procedure,
min (Note 2). Cool, dilute to volume with pretreated water, and
yields solutions which can be highly colored due to the
mix.
presence of Cr (VI) ions. Although these ions and other colored
ions in the sample solution undergo no further change in color
NOTE 2—Immersing the flasks in a boiling water bath is a preferred
means of heating them for the specified period to ensure complete color
quality upon treatment with metaperiodate ion, the following
development.
precautions must be observed when filter spectrophotometers
are used: Select a filter with maximum transmittance between 15.4 Spectrophotometry:
545 nm and 565 nm. The filter must transmit not more than 5 % 15.4.1 Multiple-Cell Spectrophotometer—Measure the cell
of its maximum at a wavelength shorter than 530 nm. The band correction using the Reference Solution (15.2) in absorption
width of the filter should be less than 30 nm when measured at cells with a 1-cm light path and using a light band centered at
50 % of its maximum transmittance. Similar restrictions apply 545 nm. Using the test cell, take the spectrophotometric
with respect to the wavelength region employed when other absorbance readings of the calibration solutions versus the
“wide-band” instruments are used. Reference Solution (15.2)
E352 − 23
15.4.2 Single-Cell Spectrophotometer—Transfer a suitable chromium is oxidized and the HCl is expelled, but avoid
portion of the Reference Solution (15.2) to an absorption cell heating to fumes of SO . Cool, add 50 mL of water, digest, if
with a 1-cm light path and adjust the spectrophotometer to the necessary, to dissolve the salts, cool, and transfer the solution
initial setting, using a light band centered at 545 nm. While to either a 100-mL or 500-mL volumetric flask as directed in
maintaining this adjustment, take the spectrophotometric ab- 16.1. Proceed to 16.1.3.
sorbance readings of the calibration solutions. 16.1.3 Cool the solution to room temperature, dilute to
volume, and mix. Allow insoluble matter to settle, or dry-filter
15.5 Calibration Curve—Follow the instrument manufac-
through a coarse paper and discard the first 15 mL to 20 mL of
turer’s instructions for generating the calibration curve. Plot
the filtrate, before taking aliquots.
the net spectrophotometric absorbance readings of the calibra-
16.1.4 Using a pipet, transfer 10 mL to 20 mL aliquots, as
tion solutions against the milligrams of manganese per 50 mL
specified in 16.1 to two 50-mL borosilicate glass volumetric
of solution.
flasks. Treat one portion as directed in 16.3. Treat the other
16. Procedure portion as directed in 16.4.1.
16.1 Test Solutions—Select and weigh a sample as follows: 16.2 Reagent Blank Solution—Carry a reagent blank
through the entire procedure using the same amounts of all
Tolerance in Dilu- Aliquot
Sample Sample tion, Volume, reagents with the sample omitted.
Manganese, % Mass, g Mass, mg mL mL
16.3 Color Development—Proceed as directed in 15.3.
0.10 to 0.5 0.80 0.5 100 20
16.4 Reference Solutions:
0.45 to 1.0 0.35 0.3 100 20
0.85 to 2.0 0.80 0.5 500 20
16.4.1 Background Color Solution—To one of the sample
0.95 to 5.0 0.80 0.5 500 10
aliquots in a 50-mL volumetric flask, add 10 mL of nitric-
Transfer it to a 300-mL Erlenmeyer flask.
phosphoric acid mixture, and heat the solution at not less than
16.1.1 For Samples Containing Not More Than 0.5 %
90 °C for 20 min to 30 min (Note 2). Cool, dilute to volume
Tungsten:
(with untreated water), and mix.
16.1.1.1 To dissolve samples that do not require HF, add 8
16.4.2 Reagent Blank Reference Solution—Transfer the re-
mL to 10 mL of HCl (1 + 1), and heat. Add HNO as needed
3 agent blank solution (16.2) to the same size volumetric flask as
to hasten dissolution, and then add 3 mL to 4 mL in excess.
used for the test solutions and transfer the same size aliquots as
When dissolution is complete, cool, then add 10 mL of HClO ;
4 used for the test solutions to two 50-mL volumetric flasks.
evaporate to fumes to oxidize chromium, if present, and to
Treat one portion as directed in 16.3 and use as reference
expel HCl. Continue fuming until salts begin to separate. Cool,
solution for test samples. Treat the other as directed in 16.4.1
add 50 mL of water, and digest if necessary to dissolve the
and use as reference solution for Background Color Solutions.
salts. Cool and transfer the solution to either a 100-mL or
16.5 Spectrophotometry—Establish the cell corrections with
500-mL volumetric flask as indicated in 16.1. Proceed to
the Reagent Blank Reference solution to be used as a reference
16.1.3.
solution for Background Color solutions. Take the spectropho-
16.1.1.2 For samples whose dissolution is hastened by HF,
tometric absorbance readings of the Background Color Solu-
add 8 mL to 10 mL of HCl (1 + 1), and heat. Add HNO and
tions and the test solutions versus the respective Reagent Blank
a few drops of HF as needed to hasten dissolution, and then add
Reference Solutions as directed in 15.4.
3 mL to 4 mL of HNO . When dissolution is complete, cool,
then add 10 mL of HClO , evaporate to fumes to oxidize
17. Calculation
chromium, if present, and to expel HCl. Continue fuming until
17.1 Convert the net spectrophotometric absorbance reading
salts begin to separate. Cool, add 50 mL of water, digest if
of the test solution and of the background color solution to
necessary to dissolve the salts, cool, and transfer the solution to
either a 100-mL or 500-mL volumetric flask as indicated in
16.1. Proceed to 16.1.3.
TABLE 1 Statistical Information—Manganese by the
16.1.2 For Samples Containing More Than 0.5 % Tungsten: Metaperiodate Spectrophotometric Method
16.1.2.1 To dissolve samples that do not require HF, add 8
Man- Repeata- Repro-
ganese bility ducibil-
mL to 10 mL of H PO , 10 mL of HClO , 5 mL to 6 mL of
3 4 4 Test Specimen
Found, (R , ity (R ,
1 2
H SO , and 3 mL to 4 mL of HNO . Heat moderately until the
2 4 3
% E173) E173)
sample is decomposed, and then heat to copious white fumes
1. Special W high-speed tool 0.160 0.012 0.035
for 10 min to 12 min or until the chromium is oxidized and the
steel (NIST 440, 0.15
Mn)
HCl is expelled, but avoid heating to fumes of SO . Cool, add
2. Tool steel (NIST 153a, 0.183 0.005 0.010
50 mL of water, and digest, if necessary, to dissolve the salts.
0.192 Mn)
Transfer the solution to either a 100-mL or 500-mL volumetric
3. W high-speed tool steel 0.268 0.010 0.034
(NIST 441, 0.27 Mn)
flask as directed in 16.1. Proceed to 16.1.3.
4. Alloy Steel (NIST, 159, 0.819 0.010 0.034
16.1.2.2 For samples whose dissolution is hastened by HF,
a, 0.807 Mn)
add 8 mL to 10 mL of H PO , 10 mL of HClO , 5 mL to 6 mL 5. Low Alloy Steel (NIST 1.91 0.02 0.04
3 4 4
100b, 1.89 Mn)
of H SO , 3 mL to 4 mL of HNO , and a few drops of HF. Heat
2 4 3
6. Stainless Steel (NIST 444, 4.60 0.04 0.13
moderately until the sample is decomposed, and then heat to
4.62 Mn)
copious white fumes for 10 min to 12 min or until the
E352 − 23
milligrams of manganese by means of the calibration curve. 24. Apparatus
Calculate the percentage of manganese as follows:
24.1 Glassware must be phosphorus- and arsenic-free. Boil
Manganese, % 5 A 2 B / C × 10 (1) the glassware with HCl and rinse with water before use. It is
~ ! ~ !
recommended that the glassware used for this determination be
where:
reserved for this use only. Many detergents contain phosphorus
A = manganese, mg, found in 50 mL of the final test
and must not be used for cleaning purposes.
solution,
B = apparent manganese, mg, found in 50 mL of the final
25. Reagents
background color solution, and
25.1 Ammonium Molybdate Solution (20 g/L)—Cautiously,
C = sample mass, g, represented in 50 mL of the final test
while stirring and cooling, add 300 mL of H SO to 500 mL of
2 4
solution.
water and cool. Add 20 g of ammonium heptamolybdate
((NH ) Mo O ·4H O), cautiously dilute to 1 L, and mix.
4 6 7 24 2
18. Precision and Bias
25.2 Ammonium Molybdate-Hydrazine Sulfate Solution—
18.1 Precision—Nine laboratories cooperated in testing this
Dilute 250 mL of the ammonium molybdate solution to 600
method and obtained the data summarized in Table 1.
mL, add 100 mL of the hydrazine sulfate solution, dilute to 1
18.2 Bias—The accuracy of this test method has been
L, and mix. Do not use a solution that has stood for more than
deemed satisfactory based upon the data for the certified
1 h.
reference materials in Table 1. Users are encouraged to use
25.3 Hydrazine Sulfate Solution (1.5 g/L)—Dissolve 1.5 g
these or similar reference materials to verify that the test
of hydrazine sulfate ((NH ) ·H SO ) in water, dilute to 1 L,
2 2 2 4
method is performing accurately in their laboratories.
and mix. Discard any unused solution after 24 h.
25.4 Phosphorus Standard Solution A (1 mL = 1.0 mg
PHOSPHORUS BY THE MOLYBDENUM BLUE
P)—Transfer 2.292 g of anhydrous disodium hydrogen phos-
SPECTROPHOTOMETRIC METHOD
phate (Na HPO ), previously dried to constant mass at 105 °C,
2 4
to a 500-mL volumetric flask; dissolve in about 100 mL of
19. Scope
water, dilute to volume, and mix.
19.1 This test method covers the determination of phospho-
25.5 Phosphorus Standard Solution B (1 mL = 0.01 mg
rus from 0.002 % to 0.05 %.
P)—Using a pipet, transfer 10 mL of Solution A (1 mL = 1.0
mg P) to a 1-L volumetric flask, add 50 mL of HClO (1 + 5),
20. Summary of Method
dilute to volume, and mix.
20.1 The sample is dissolved in mixed acids and the
25.6 Phosphorus Standard Solution C (1 mL = 0.10 mg
solution is fumed with HClO . Ammonium molybdate is added
P)—Using a pipet, transfer 50 mL of Solution A (1 mL = 1.0
to react with the phosphorus to form the heteropoly phospho-
mg P) to a 500-mL volumetric flask, add 50 mL of HClO (1
molybdate. This species is then reduced with hydrazine sulfate
+ 5), dilute to volume, and mix.
to form the molybdenum blue complex. Spectrophotometric
absorbance measurement is made at 650 nm or 825 nm, 25.7 Sodium Sulfite Solution (100 g/L)—Dissolve 100 g of
depending upon the concentration. sodium sulfite (Na SO ) in water, dilute to 1 L, and mix.
2 3
26. Preparation of Calibration Curve for Concentrations
21. Concentration Range
from 0.005 mg/100 mL to 0.05 mg/100 mL
21.1 The recommended concentration range is from 0.005
26.1 Calibration Solutions—Using pipets, transfer 5 mL, 10
mg to 0.05 mg of phosphorus per 100 mL of solution when
mL, 15 mL, 25 mL, and 50 mL of Phosphorus Standard
measured at 825 nm and from 0.05 mg to 0.3 mg of phosphorus
Solution B (1 mL = 0.01 mg P) to 100-mL volumetric flasks.
per 100 mL of solution when measured at 650 nm, using a
Add 20 mL of HClO , dilute to volume, and mix. Using a pipet,
1-cm cell. 4
transfer 10 mL of each solution to a 100-mL borosilicate glass
NOTE 3—This test method has been written for cells having a 1-cm light
path. Cells having other dimensions may be used, provided suitable
volumetric flask. Proceed as directed in 26.3.
adjustments can be made in the amounts of sample and reagents used.
26.2 Reagent Blank—Transfer 12 mL of HClO (1 + 5) to a
100-mL borosilicate glass volumetric flask.
22. Stability of Color
26.3 Color Development:
22.1 The molybdenum blue complex is stable for at least 2
26.3.1 Add 15 mL of Na SO solution, boil gently for 30 s,
2 3
h.
and add 50 mL of ammonium molybdate-hydrazine sulfate
solution that has been prepared within the hour.
23. Interferences
26.3.2 Heat the solutions at not less than 90 °C for 20 min,
23.1 None of the elements usually present interfere except
quickly cool, dilute to volume, and mix.
arsenic which is removed by volatilization as the bromide. The
NOTE 4—Immersing the flasks in a boiling water bath is the preferred
interference of tungsten at compositions greater than 0.5 % is
means of heating them for complete color development.
avoided by proceeding directly with a small sample mass rather
than an aliquot portion of a larger sample. 26.4 Reference Solution—Water.
E352 − 23
26.5 Spectrophotometry: 27.2.1 Test Solution:
26.5.1 Multiple-Cell Spectrophotometer—Measure the re- 27.2.1.1 Transfer 0.100-g samples, weighed to the nearest
agent blank (which includes the cell correction) versus the 0.1 mg, to two 100-mL Erlenmeyer flasks.
reference solution (26.4) using absorption cells with a 1-cm 27.2.1.2 Add 5 mL of a mixture of 1 volume of HNO and
light path and using a light band centered at 825 nm. Using the 3 volumes of HCl. When the reaction has ceased, add 2.5 mL
test cell, take the spectrophotometric absorbance readings of of HClO and 5 mL of HBr (1 + 4). Evaporate the solutions to
the calibration solutions versus the reference solution. copious white fumes; then, without delay, fume strongly
26.5.2 Single-Cell Spectrophotometer—Transfer a suitable enough to cause the white fumes to clear the neck of the flasks,
portion of the reference solution (26.4) to an absorption cell and continue at this rate for 1 min.
with a 1-cm light path and adjust the spectrophotometer to the 27.2.1.3 Cool the solutions, and add 10 mL of water. Filter
initial setting using a light band centered at 825 nm. While through a 9-cm fine paper collecting the filtrate in a 100-mL
maintaining this adjustment, take the spectrophotometric ab- borosilicate glass volumetric flask. Wash the paper and in-
sorbance readings of the reagent blank solution and of the soluble matter 5 times with 3-mL portions of water. Treat one
calibration solutions. solution as directed in 27.2.3 and the other as directed in
27.2.4.
26.6 Calibration Curve—Follow the instrument manufac-
27.2.2 Reagent Blank Solution—Proceed as directed in
turer’s instructions for generating the calibration curve. Plot
27.2.1.2 and 27.2.1.3.
the net spectrophotometric absorbance readings of the calibra-
27.2.3 Color Development—Proceed as directed in 26.3.
tion solutions against the milligrams of phosphorus per 100 mL
27.2.4 Reference Solutions:
of solution.
27.2.4.1 Water—Use this as the reference solution for the
reagent blank solution.
27. Procedure
27.2.4.2 Background Color Reference Solution—Add 15
27.1 For Samples Containing Less Than 0.5 % Tungsten:
mL of Na SO solution to the second 10-mL portion obtained
2 3
27.1.1 Test Solution:
in 27.2.1.3. Boil gently for 30 s, add 50 mL of H SO (3 + 37),
2 4
27.1.1.1 Transfer a 1.0-g sample, weighed to the nearest 0.5
cool, dilute to volume, and mix. Use this as the reference
mg, to a 250-mL Erlenmeyer flask.
solution for the test solution.
27.1.1.2 Add 15 mL of a freshly prepared mixture of 1
27.2.5 Spectrophotometry—Proceed as directed in 27.1.5.
volume of HNO and 3 volumes of HCl, slowly and in small
portions. When the reaction has ceased, add 10 mL of HClO
28. Calculation
and evaporate to fumes. Remove the flask immediately to
28.1 Convert the net spectrophotometric absorbance reading
avoid undue loss of HClO , cool, and add 20 mL of HBr (1 +
of the test solution and of the reagent blank solution to
4). Evaporate the solution to copious white fumes and then,
milligrams of phosphorus by means of the appropriate calibra-
without delay, fume strongly enough to cause the white fumes
tion curve. Calculate the percent of phosphorus as follows:
to clear the neck of the flask, and continue at this rate for 1 min.
Phosphorus,% 5 ~A 2 B!⁄~C × 10! (2)
27.1.1.3 Cool the solution, add 60 mL of HClO (1 + 5), and
swirl to dissolve the salts. Transfer to a 100-mL volumetric
where:
flask, cool, dilute to volume, and mix. Allow insoluble matter
A = phosphorus found in 100 mL of the final test solution,
to settle or dry filter the solution. Using a pipet, transfer 10-mL
mg,
portions to two 100-mL borosilicate glass volumetric flasks;
B = phosphorus found in 100 mL of the final reagent blank
treat one as directed in 27.1.3 and the other as directed in
solution, mg, and
27.1.4.2.
C = sample represented in 100 mL of the final test solution,
27.1.2 Reagent Blank Solution—Carry a reagent blank
g.
through the entire procedure using the same amount of all
reagents with the sample omitted.
29. Precision and Bias
27.1.3 Color Development—Proceed with one of the 10-mL
29.1 Precision—Eight laboratories cooperated in testing this
portions obtained in 27.1.1.3, as directed in 26.3.
method and obtained the data summarized in Table 2.
27.1.4 Reference Solutions:
27.1.4.1 Water—Use this as the reference solution for the
reagent blank solution. TABLE 2 Statistical Information—Phosphorus – Molybdenum
Blue – Spectrophotometric Method
27.1.4.2 Background Color Reference Solution—Add 15
Phos- Repeata- Repro-
mL of Na SO solution to the second 10-mL portion obtained
2 3
phorus bility ducibil-
in 27.1.1.3. Boil gently for 30 s, add 50 mL of H SO (3 + 37), Test Specimen
2 4
Found, (R , ity (R ,
1 2
cool, dilute to volume, and mix. Use this as the reference
% E173) E173)
solution for the test solution.
1. Tool steel 5Mo-6W-4Cr-2V 0.029 0.011 0.008
(NIST 132a, 0.029 P)
27.1.5 Spectrophotometry—Take the spectrophotometric
2. Tool steel 8Co-9Mo-2W- 0.023 0.008 0.007
absorbance readings of the reagent blank solution and of the
4Cr-2V (NIST 153a,
test solution (using the respective reference solutions) as
0.023 P)
3. Tool steel 18W-4Cr-1V 0.022 0.005 0.007
directed in 26.5.
(NIST 50c, 0.022 P)
27.2 For Samples Containing More Than 0.5 % Tungsten:
E352 − 23
29.2 Bias—The accuracy of this test method has been to the papers, and scrub the beakers thoroughly with a
deemed satisfactory based upon the data for the certified rubber-tipped rod. Wash the papers and precipitates alternately
reference materials in Table 2. Users are encouraged to use with 3 mL to 5 mL portions of hot HCl (1 + 19) and hot water,
these or similar reference materials to verify that the test for a total of 6 times. Finally wash the papers twice with H SO
2 4
method is performing accurately in their laboratories. (1 + 49). Transfer the papers to platinum crucibles.
48.2.4 Dry the papers and heat at 600 °C until the carbon is
removed. Finally ignite at 1100 °C to 1150 °C to constant mass
SULFUR BY THE GRAVIMETRIC METHOD
(at least 30 min). Cool in a desiccator and weigh.
48.2.5 Add enough H SO (1 + 1) to moisten the SiO , and
2 4 2
(This method, which consisted of Sections 29 through 35 of
add 3 mL to 5 mL of HF. Evaporate to dryness and then heat
this standard, was discontinued in 1988.)
at a gradually increasing rate until H SO is removed. Ignite
2 4
SULFUR BY THE COMBUSTION-IODATE
for 15 min at 1100 °C to 1150 °C, cool in a desiccator, and
TITRATION METHOD weigh.
48.2.6 Calculate the percent of silicon as follows:
(This method, which consisted of Sections 36 through 44 of
Silicon,% 5 @~A 2 B! 2 ~C 2 D!# × 0.4674⁄E × 100 (3)
this standard, was discontinued in 2012.)
where:
A = initial mass of crucible plus impure SiO when 65 mL of
SILICON BY THE GRAVIMETRIC METHOD
HClO was taken, g,
45. Scope B = final mass of crucible plus impurities when 65 mL of
HClO was taken, g,
45.1 This method covers the determination of silicon from
C = initial mass of crucible plus impure SiO when 15 mL of
0.10 % to 2.50 %.
HClO was taken, g,
D = final mass of crucible plus impurities when 15 mL of
46. Summary of Method
HClO was taken, g, and
46.1 After dissolution of the sample, silicic acid is dehy-
E = nominal mass (80 g) of 50 mL of HClO .
drated by fuming with H SO or HClO . The solution is
2 4 4
48.3 Sodium Silicate Solution—Transfer 11.0 g of sodium
filtered, and the impure silica is ignited and weighed. The silica
silicate (Na SiO ·9H O) to a 400-mL beaker. Add 150 mL of
is then volatilized with HF. The residue is ignited and weighed; 2 3 2
water and dissolve the salt. Filter through a medium paper,
the loss in mass represents silica.
collecting the filtrate in a 1-L volumetric flask, dilute to
47. Interferences
volume, and mix. Store in a polyethylene bottle. Use this
solution to determine the suitability of the HClO .
47.1 The elements normally present do not interfere if their
compositions are under the maximum limits shown in 1.1.
48.4 Tartaric Acid Solution (20.6 g/L)—Dissolve 20.6 g of
tartaric acid (C H O ) in water, dilute to 1 L, and filter.
4 6 6
48. Reagents
48.5 Water—Use freshly prepared Type II water known to
48.1 The analyst should ensure by analyzing blanks and
be free of silicon. Water distilled from glass, demineralized in
other checks that possible silicon contamination of reagents
columns containing silicon compounds, or stored for extended
will not significantly bias the results.
periods in glass, or combination thereof, has been known to
48.2 Perchloric Acid (HClO ):
absorb silicon.
48.2.1 Select a lot of HClO that contains not more than
49. Procedure
0.0002 % silicon for the analysis of samples containing silicon
in the range from 0.02 % to 0.10 % and not more than 0.0004
49.1 Select and weigh a sample as follows:
% silicon for samples containing more than 0.10 % by
Dehydrating Acid, mL
determining duplicate values for silicon as directed in 48.2.2 – Tolerance in
Sample Sample H SO
2 4
48.2.6.
Silicon, % Mass, g Mass, mg (1 + 4) HClO
48.2.2 Transfer 15 mL of HClO (Note 5) to each of two
4 0.1 to 0.1 4.0 4 150 60
400-mL beakers. To one of the beakers transfer an additional 1.0 to 1.75 3.0 3 100 50
1.75 to 2.50 2.0 2 100 40
50 mL of HClO . Using a pipet, transfer 20 mL of Na SiO
4 2 3
Transfer it to a 400-mL beaker or a 300-mL porcelain
solution (1 mL = 1.00 mg Si) to each of the beakers. Evaporate
casserole. Proceed as directed in 49.2 if tungsten is greater than
the solutions to fumes and heat for 15 min to 20 min at such a
0.5% or if tungsten is less than 0.5%, proceed as directed in
rate that HClO refluxes on the sides of the beakers. Cool
49.2 or 49.3.
sufficiently, and add 100 mL of water (40 °C to 50 °C).
49.2 Sulfuric Acid Dehydration (H SO ):
2 4
NOTE 5—The 15-mL addition of HClO can be from the same lot as the
49.2.1 Add amounts of HCl or HNO , or mixtures and
one to be tested. Once a lot has been established as having less than 0.0002
% silicon, it should preferably be used for the 15-mL addition in all
dilutions of these acids, that are sufficient to dissolve the
subsequent tests of other lots of acid.
sample; and then add the H SO (1 + 4) as specified in 49.1,
2 4
48.2.3 Add paper pulp and filter immediately, using low-ash and cover. Heat until dissolution is complete. Remove and
11-cm medium-porosity filter papers. Transfer the precipitates rinse the cover glass; substitute a ribbed cover glass.
E352 − 23
49.2.2 Evaporate until salts begin to separate; at this point 50. Calculation
evaporate the solution rapidly to the first appearance of fumes
50.1 Calculate the percent of silicon as follows:
and fume strongly for 2 min to 3 min. Cool sufficiently, and add
Silicon,% 5 @ A 2 B × 0.4674 ⁄C# × 100 (4)
~~ ! !
100 mL of water (40 °C to 50 °C). Stir to dissolve the salts and
heat, if necessary, but do not boil. Proceed immediately as
where:
directed in 49.4.
A = initial mass of crucible and impure SiO , g,
B = final mass of crucible and residue, g, and
49.3 Perchloric Acid (HClO ) Dehydration:
C = sample used, g.
49.3.1 Add amounts of HCl or HNO , or mixtures and
dilutions of these acids, which are sufficient to dissolve the
51. Precision and Bias
sample, and cover. Heat until dissolution is complete. Add
51.1 Precision—Eleven laboratories cooperated in testing
HNO to provide a total of 35 mL to 40 mL, followed by
this method and obtained the data summarized in Table 3.
HClO as specified in the table in 49.1. Remove and rinse the
Samples with tungsten below 0.5 % were not available for
cover glass; substitute a ribbed cover glass.
testing the HClO dehydration procedure; neither were samples
49.3.2 Evaporate the solution to fumes and heat for 15 min 4
available with tungsten greater than 0.5 % for testing the
to 20 min at such a rate that the HClO refluxes on the sides of
H SO dehydration procedure near the upper limit of the scope.
the container. Cool sufficiently and add 100 mL of water (40 °C 2 4
to 50 °C). Stir to dissolve the salts and heat to boiling. If the
51.2 Bias—Either this method has no bias, or this method is
sample solution contains more than 100 mg of chromium, add,
subject to bias under certain sample conditions. Only one
while stirring, 1 mL of tartaric acid solution for each 25 mg of
certified reference material was available for testing during the
chromium.
interlaboratory study, see Table 3. The user of this method is
encouraged to utilize accepted reference materials, if available,
49.4 Add paper pulp and filter immediately, on a low-ash
to determine the presence or absence of bias.
11-cm medium-porosity filter paper. Collect the filtrate in a
600-mL beaker. Transfer the precipitate to the paper, and scrub
the container thoroughly with a rubber-tipped rod. Wash the
COBALT BY THE ION-EXCHANGE—
paper and precipitate alternately with 3 mL to 5 mL portions of
POTENTIOMETRIC TITRATION METHOD
hot HCl (1 + 19) and hot water until iron salts are removed but
for not more than a total of ten washings. If the HClO
52. Scope
dehydration method was followed, wash the paper twice more
52.1 This method covers the determination of cobalt from
with H SO (1 + 49), but do not collect these washings in the
2 4
2 % to 14 %.
filtrate; discard the washings. Transfer the paper to a platinum
crucible and reserve.
53. Summary of Method
49.5 Add 15 mL of HNO to the filtrate, stir, and evaporate
3 53.1 Cobalt is separated from interfering elements by selec-
in accordance with either 49.2 or 49.3, depending upon the
tive elution from an anion-exchange column using HCl. The
dehydrating acid used. Filter immediately, using a low-ash,
cobalt is oxidized to the trivalent state with ferricyanide, and
9-cm 100-porosity filter paper, and wash as directed in 49.4.
the excess ferricyanide is titrated potentiometrically with
cobalt solution.
49.6 Transfer the paper and precipitate to the reserved
platinum crucible. Dry the papers and then heat the crucible at
54. Interferences
600 °C until the carbon is removed. Finally ignite at 1100 °C
54.1 The elements normally present do not interfere if their
to 1150 °C to constant mass (at least 30 min). Cool in a
compositions are under the maximum limits shown in 1.1.
desiccator and weigh.
49.7 Add enough H SO (1 + 1) to moisten the impure
2 4 55. Apparatus
SiO , and add 3 mL to 5 mL of HF. Evaporate to dryness and
55.1 Ion-Exchange Column, approximately 25 mm in diam-
then heat at a gradually increasing rate until H SO is removed.
2 4
eter and 300 mm in length, tapered at one end, and provided
Ignite at 1100 °C to 1150 °C for 15 min, cool in a desiccator,
with a stopcock to control the flow rate, and a second, lower
and weigh. If the sample contains more than 0.5 % tungsten,
stopcock to stop the flow. A Jones Reductor (Fig. 1) may be
ignite at 750 °C instead of 1100 °C to 1150 °C after
adapted to this method. A reservoir for the eluants may be
volatilization of SiO .
added at the top of the column.
55.2 pH meter, with a platinum and a saturated calomel
electrode.
TABLE 3 Statistical Information—Silicon – Gravimetric Method
56. Reagents
Silicon
Repeatability Reproducibility
Test Specimen Found,
56.1 Ammonium Citrate Solution (200 g/l)—Dissolve 200 g
(R , E173) (R , E173)
1 2
%
of di–ammonium hydrogen citrate in water and dilute to 1 L.
H SO Dehydration
2 4
1. Tool steel 5Mo-6W-4Cr-2V 0.193 0.019 0.031
56.2 Bromine
(NIST 132a, 0.19 Si)
56.3 Cobalt, Standard Solution (1mL = 1.5 mg of Co):
E352 − 23
FIG. 1 Jones Reductor
56.3.1 Preparation—Dry a weighing bottle in an oven at retained on the screen, periodically, if necessary, to avoid
130 °C for 1 h, cool in a desiccator, and weigh. Transfer 3.945 undue clogging of the openings. When the bulk of the collected
g of cobalt sulfate (CoSO ) that has been heated at 550 °C for resin has settled, decant the water and transfer approximately
1 h to the weighing bottle. Dry the bottle and contents at 130 100 mL of resin to a 400-mL beaker. Add 200 mL of HCl (1 +
°C for 1 h, cool in desiccator, stopper the bottle, and weigh. 19), stir vigorously, allow the resin to settle for 4 min to 6 min,
The difference in mass is the amount of CoSO taken. Transfer decant 150 mL to 175 mL of the suspension, and discard.
the weighed CoSO to a 400-mL beaker, rinse the weighing Repeat the treatment with HCl (1 + 19) twice more, and reserve
bottle with water, and transfer the rinsings to the beaker. Add the coarser resin for the column preparation.
150 mL of water and 20 mL of HNO , and heat to dissolve the
56.4.2 Prepare the column as follows: Place a 10-mm to
salts. Cool, transfer to a 1-L volumetric flask, dilute to volume,
20-mm layer of glass wool or polyvinyl chloride plastic fiber in
and mix.
the bottom of the column, and add a sufficient amount of the
56.3.2 Standardization—Calculate the cobalt concentration
prepared resin to fill the column to a height of approximately
as follows:
140 mm. Place a 20-mm layer of glass wool or polyvinyl
chloride plastic fiber at the top of the resin bed to protect it
Cobalt, mg⁄mL 5 mass of CoSO , g × 0.38026 (5)
from being carried into suspension when the solutions are
56.4 Ion-Exchange Resin:
added. While passing a minimum of 35 mL of HCl (7 + 5)
56.4.1 Use an anion exchange resin of the alkyl quaternary
through the column, with the hydrostatic head 100 mm above
ammonium type (chloride form) consisting of spherical beads
the top of the resin bed, adjust the flow rate to not more than
having a nominal crosslinkage of 8 %, and 0.075-mm to
3.0 mL per min. Drain to 10 mm to 20 mm above the top of the
0.037-mm (200-nominal to 400-nominal mesh) size. To re-
resin bed and then close the lower stopcock.
move those beads greater than about 180-μm in diameter as
well as the excessively fine beads, treat the resin as follows: NOTE 6—The maximum limits of 0.125 g of cobalt and 0.500 g in the
sample solution take into account the exchange capacity of the resin, the
Transfer a supply of the resin to a beaker, cover with water, and
physical dimensions of the column, and the volume of eluants.
allow sufficient time (at least 30 min) for the beads to undergo
maximum swelling. Place a 180-μm (No. 80) screen, 150 mm 56.5 Potassium Ferricyanide, Standard Solution (1 mL =
in diameter over a 2-L beaker. Prepare a thin slurry of the resin
3.0 mg of Co):
and pour it onto the screen. Wash the fine beads through the
56.5.1 Dissolve 16.68 g of potassium ferricyanide
screen, using a small stream of water. Discard the beads
(K Fe(CN) ) in water and dilute to 1 L. Store the solut
...


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.
´1
Designation: E352 − 18 E352 − 23
Standard Test Methods for
Chemical Analysis of Tool Steels and Other Similar Medium-
and High-Alloy Steels
This standard is issued under the fixed designation E352; 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.
ε NOTE—An editorial correction was made in Table 5 in February 2022.
1. Scope
1.1 These test methods cover the chemical analysis of tool steels and other similar medium- and high-alloy steels having chemical
compositions within the following limits:
Element Composition Range, %
Aluminum 0.005 to 1.5
Boron 0.001 to 0.10
Carbon 0.03 to 2.50
Chromium 0.10 to 14.0
Cobalt 0.10 to 14.0
Copper 0.01 to 2.0
Lead 0.001 to 0.01
Manganese 0.10 to 15.00
Molybdenum 0.01 to 10.00
Nickel 0.02 to 4.00
Nitrogen 0.001 to 0.20
Phosphorus 0.002 to 0.05
Silicon 0.10 to 2.50
Sulfur 0.002 to 0.40
Tungsten 0.01 to 21.00
Vanadium 0.02 to 5.50
1.2 The test methods in this standard are contained in the sections indicated below:
Sections
Carbon, Total, by the Combustion—
Thermal Conductivity Method—
Discontinued 1986 125–135
Carbon, Total, by the Combustion Gravimetric
Method—Discontinued 2012 78–88
Chromium by the Atomic Absorption
Spectrometry Method (0.006 % to 1.00 %) 174–183
Chromium by the Peroxydisulfate
Oxidation—Titration Method (0.10 % to 14.00 %) 184–192
Chromium by the Peroxydisulfate-Oxidation
Titrimetric Method—Discontinued 1980 117–124
These test methods are under the jurisdiction of the ASTM Committee E01 on Analytical Chemistry for Metals, Ores, and Related Materials and are the direct
responsibility of Subcommittee E01.01 on Iron, Steel, and Ferroalloys.
Current edition approved July 1, 2018Nov. 15, 2023. Published September 2018December 2023. Originally approved in 1968. Last previous edition approved in 20132018
ɛ1
as E352 – 13.E352 – 18 . DOI: 10.1520/E0352-18E01.10.1520/E0352-23.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E352 − 23
Sections
Cobalt by the Ion-Exchange—
Potentiometric Titration Method (2 % to 14 %) 52–59
Cobalt by the Nitroso-R-Salt
Spectrophotometric Method (0.10 % to 5.0 %) 60–69
Copper by the Neocuproine
Spectrophotometric Method (0.01 % to 2.00 %) 89–98
Copper by the Sulfide Precipitation-
Electrodeposition Gravimetric Method (0.01 % to 2.0 %) 70–77
Lead by the Ion-Exchange—Atomic
Absorption Spectrometry Method (0.001 % to 0.01 %) 99–108
Manganese by the Periodate
Spectrophotometric Method (0.10 % to 5.00 %) 9–18
Molybdenum by the Ion Exchange–
8-Hydroxyquinoline Gravimetric Method 203–210
Molybdenum by the Thiocyanate
Spectrophotometric Method (0.01 % to 1.50 %) 162–173
Nickel by the Dimethylglyoxime
Gravimetric Method (0.1 % to 4.0 %) 144–151
Phosphorus by the Alkalimetric Method (0.01 % to 0.05 %) 136–143
Phosphorus by the Molybdenum Blue
Spectrophotometric Method (0.002 % to 0.05 %) 19–29
Silicon by the Gravimetric Method (0.10 % to 2.50 %) 45–51
Sulfur by the Gravimetric
Method—Discontinued 1988 29–35
Sulfur by the Combustion-Iodate
Titration Method—Discontinued 2012 36–44
Sulfur by the Chromatographic
Gravimetric Method—Discontinued 1980 109–116
Tin by the Solvent Extraction—
Atomic Absorption Spectrometry Method (0.002 % to 0.10 %) 152–161
Vanadium by the Atomic
Absorption Spectrometry Method (0.006 % to 0.15 %) 193–202
1.3 Test methods for the determination of carbon and sulfur not included in this standard can be found in Test Methods E1019.
1.4 Some of the composition ranges given in 1.1 are too broad to be covered by a single test method and therefore this standard
contains multiple test methods for some elements. The user must select the proper test method by matching the information given
in the Scope and Interference sections of each test method with the composition of the alloy to be analyzed.
1.5 The values stated in SI units are to be regarded as standard.
1.6 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. Specific hazards statements are given in Section 6 and in special “Warning” paragraphs
throughout these test methods.
1.7 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:
D1193 Specification for Reagent Water
E29 Practice for Using Significant Digits in Test Data to Determine Conformance with Specifications
E50 Practices for Apparatus, Reagents, and Safety Considerations for Chemical Analysis of Metals, Ores, and Related Materials
E60 Practice for Analysis of Metals, Ores, and Related Materials by Spectrophotometry
E135 Terminology Relating to Analytical Chemistry for Metals, Ores, and Related Materials
E173 Practice for Conducting Interlaboratory Studies of Methods for Chemical Analysis of Metals (Withdrawn 1997)
E350 Test Methods for Chemical Analysis of Carbon Steel, Low-Alloy Steel, Silicon Electrical Steel, Ingot Iron, and Wrought
Iron
E351 Test Methods for Chemical Analysis of Cast Iron—All Types
For referenced ASTM standards, visit the ASTM website, www.astm.org, or contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
The last approved version of this historical standard is referenced on www.astm.org.
E352 − 23
E353 Test Methods for Chemical Analysis of Stainless, Heat-Resisting, Maraging, and Other Similar Chromium-Nickel-Iron
Alloys
E354 Test Methods for Chemical Analysis of High-Temperature, Electrical, Magnetic, and Other Similar Iron, Nickel, and
Cobalt Alloys
E882 Guide for Accountability and Quality Control in the Chemical Analysis Laboratory
E1019 Test Methods for Determination of Carbon, Sulfur, Nitrogen, and Oxygen in Steel, Iron, Nickel, and Cobalt Alloys by
Various Combustion and Inert Gas Fusion Techniques
E1024 Guide for Chemical Analysis of Metals and Metal Bearing Ores by Flame Atomic Absorption Spectrophotometry
(Withdrawn 2004)
E1601 Practice for Conducting an Interlaboratory Study to Evaluate the Performance of an Analytical Method
E1806 Practice for Sampling Steel and Iron for Determination of Chemical Composition
2.2 Other Document:
ISO 5725 Precision of Test Methods—Determination of Repeatability and Reproducibility for Inter-Laboratory Tests
3. Terminology
3.1 For definitions of terms used in these test methods, refer to Terminology E135.
4. Significance and Use
4.1 These test methods for the chemical analysis of metals and alloys are primarily intended as referee methods to test such
materials for compliance with compositional specifications particularly those under the jurisdiction of ASTM Committee A01 on
Steel, Stainless Steel, and Related Alloys. It is assumed that all who use these test methods will be trained analysts capable of
performing common laboratory procedures skillfully and safely. It is expected that work will be performed in a properly equipped
laboratory under appropriate quality control practices such as those described in Guide E882.
5. Apparatus, Reagents, and Instrumental Practices
5.1 Apparatus—Specialized apparatus requirements are listed in the “Apparatus” Section in each method.
5.1.1 In the methods specifying spectrophotometric testing, the cells utilized to contain the reference material solutions and sample
solutions in spectrophotometers are referred to as “absorption cells”. Please note that the radiant energy passed through the cells
can be measured as absorbance or transmittance. These methods refer to absorbance measurements. Refer to Practices E60 for
details.
5.2 Reagents:
5.2.1 Purity of Reagents—Reagent grade chemicals shall be used in all tests. Unless otherwise indicated, all reagents used in these
test methods shall conform to the “Reagent Grade” Specifications of the American Chemical Society.Committee on Analytical
Reagents of the American Chemical Society where such specifications are available. Other chemicals may be used, provided it
is first ascertained that they are of sufficiently high purity to permit their use without adversely affecting the expected performance
of the determination, as indicated in the section on “Precision and Bias.”
5.2.2 Purity of Water—Unless otherwise indicated, references to water shall be understood to mean reagent water as conforming
to Type I or Type II of Specification D1193. Type III or IV may be used if they effect no measurable change in the blank or sample.
5.3 Spectrophotometric Practice—Spectrophotometric practice prescribed in these test methods shall conform to Practice E60.
6. Hazards
6.1 For precautions to be observed in the use of certain reagents and equipment in these methods, refer to Practices E50.
Available from American National Standards Institute (ANSI), 25 W. 43rd St., 4th Floor, New York, NY 10036, http://www.ansi.org.
“Reagent Chemicals, American Chemical Society Specifications,” American Chemical Society, Washington, DC. DC, www.acs.org. For suggestions on the testing of
Reagents not listed by the American Chemical Society, see the United States Pharmacopeia and National Formulary, U.S. Pharmacopeial Convention, Inc. (USPC),
Rockville, MD.MD, www.usp.org.
E352 − 23
7. Sampling
7.1 For procedures to sample the material, refer to Practice E1806.
8. Interlaboratory Studies and Rounding Calculated Values
8.1 These test methods have been evaluated in accordance with Practice E173 (withdrawn 1997) or ISO 5725. Practice E173 has
been replaced by Practice E1601. The Reproducibility, R2, of E173 corresponds to the Reproducibility Index, R, of E1601. The
Repeatability, R1, of E173 corresponds to the Repeatability Index, r, of E1601.
8.2 Rounding of test results obtained using these test methods shall be performed as directed in ASTM E29, Rounding Method,
unless an alternative rounding method is specified by the customer or applicable material specification.
MANGANESE BY THE METAPERIODATE SPECTROPHOTOMETRIC METHOD
9. Scope
9.1 This method covers the determination of manganese from 0.10 % to 5.00 %.
10. Summary of Method
10.1 Manganous ions are oxidized to permanganate ions by treatment with periodate. Tungsten when present at compositions
greater than 0.5 % is kept in solution with phosphoric acid. Solutions of the samples are fumed with HClO so that the effect of
periodate is limited to the oxidation of manganese. Spectrophotometric absorbance measurement is made at 545 nm.
11. Concentration Range
11.1 The recommended concentration range is 0.15 mg to 0.8 mg of manganese per 50 mL of solution, using a 1-cm cell (Note
1) and a spectrophotometer with a band width of 10 nm or less.
NOTE 1—This method has been written for cells having a 1-cm light path and a “narrow-band” instrument. The concentration range depends upon band
width and spectral region used as well as cell optical path length. Cells having other dimensions may be used, provided suitable adjustments can be made
in the amounts of sample and reagents used.
12. Stability of Color
12.1 The color is stable for at least 24 h.
13. Interferences
13.1 HClO treatment, which is used in the procedure, yields solutions which can be highly colored due to the presence of Cr (VI)
ions. Although these ions and other colored ions in the sample solution undergo no further change in color quality upon treatment
with metaperiodate ion, the following precautions must be observed when filter spectrophotometers are used: Select a filter with
maximum transmittance between 545 nm and 565 nm. The filter must transmit not more than 5 % of its maximum at a wavelength
shorter than 530 nm. The band width of the filter should be less than 30 nm when measured at 50 % of its maximum transmittance.
Similar restrictions apply with respect to the wavelength region employed when other “wide-band” instruments are used.
13.2 The spectral transmittance curve of permanganate ions exhibits two useful minima, one at approximately 526 nm, and the
other at 545 nm. The latter is recommended when a “narrow-band” spectrophotometer is used.
13.3 Tungsten, when present in amounts of more than 0.5 % interferes by producing a turbidity in the final solution. A special
procedure is provided for use with samples containing more than 0.5 % tungsten which eliminates the problem by preventing the
precipitation of the tungsten.
E352 − 23
14. Reagents
14.1 Manganese, Standard Solution (1 mL = 0.032 mg Mn)—Transfer the equivalent of 0.4000 g of assayed, high-purity
manganese (purity: 99.99 % minimum), to a 500-mL volumetric flask and dissolve in 20 mL of HNO by heating. Cool, dilute to
volume, and mix. Using a pipet, transfer 20 mL to a 500-mL volumetric flask, dilute to volume, and mix.
14.2 Nitric-Phosphoric Acid Mixture—Cautiously, while stirring, add 100 mL of HNO and 400 mL of H PO to 400 mL of water.
3 3 4
Cool, dilute to 1 L, and mix. Prepare fresh as needed.
14.3 Potassium Metaperiodate Solution (7.5 g/L)—Dissolve 7.5 g of potassium metaperiodate (KIO ) in 200 mL of hot HNO
4 3
(1 + 1), add 400 mL of H PO , cool, dilute to 1 L, and mix.
3 4
14.4 Water, Pretreated with Metaperiodate—Add 20 mL of KIO solution to 1 L of water, mix, heat at not less than 90 °C for 20
min to 30 min, and cool. Use this water to dilute solutions to volume that have been treated with KIO solution to oxidize
manganese, and thus avoid reduction of permanganate ions by any reducing agents in the untreated water. (Caution—Avoid the
use of this water for other purposes.)
15. Preparation of Calibration Curve
15.1 Calibration Solutions—Using pipets, transfer 5 mL, 10 mL, 15 mL, 20 mL, and 25 mL of manganese standard solution (1
mL = 0.032 mg Mn) to 50-mL borosilicate glass volumetric flasks, and, if necessary, dilute to approximately 25 mL. Proceed as
directed in 15.3.
15.2 Reference Solution—Transfer approximately 25 mL of water to a 50-mL borosilicate glass volumetric flask. Proceed as
directed in 15.3.
15.3 Color Development—Add 10 mL of KIO solution, and heat the solutions at not less than 90 °C for 20 min to 30 min (Note
2). Cool, dilute to volume with pretreated water, and mix.
NOTE 2—Immersing the flasks in a boiling water bath is a preferred means of heating them for the specified period to ensure complete color development.
15.4 Spectrophotometry:
15.4.1 Multiple-Cell Spectrophotometer—Measure the cell correction using the Reference Solution (15.2) in absorption cells with
a 1-cm light path and using a light band centered at 545 nm. Using the test cell, take the spectrophotometric absorbance readings
of the calibration solutions versus the Reference Solution (15.2)
15.4.2 Single-Cell Spectrophotometer—Transfer a suitable portion of the Reference Solution (15.2) to an absorption cell with a
1-cm light path and adjust the spectrophotometer to the initial setting, using a light band centered at 545 nm. While maintaining
this adjustment, take the spectrophotometric absorbance readings of the calibration solutions.
15.5 Calibration Curve—Follow the instrument manufacturer’s instructions for generating the calibration curve. Plot the net
spectrophotometric absorbance readings of the calibration solutions against the milligrams of manganese per 50 mL of solution.
16. Procedure
16.1 Test Solutions—Select and weigh a sample as follows:
Tolerance in Dilu- Aliquot
Sample Sample tion, Volume,
Manganese, % Mass, g Mass, mg mL mL
0.10 to 0.5 0.80 0.5 100 20
0.45 to 1.0 0.35 0.3 100 20
0.85 to 2.0 0.80 0.5 500 20
0.95 to 5.0 0.80 0.5 500 10
Transfer it to a 300-mL Erlenmeyer flask.
E352 − 23
16.1.1 For Samples Containing Not More Than 0.5 % Tungsten:
16.1.1.1 To dissolve samples that do not require HF, add 8 mL to 10 mL of HCl (1 + 1), and heat. Add HNO as needed to hasten
dissolution, and then add 3 mL to 4 mL in excess. When dissolution is complete, cool, then add 10 mL of HClO ; evaporate to
fumes to oxidize chromium, if present, and to expel HCl. Continue fuming until salts begin to separate. Cool, add 50 mL of water,
and digest if necessary to dissolve the salts. Cool and transfer the solution to either a 100-mL or 500-mL volumetric flask as
indicated in 16.1. Proceed to 16.1.3.
16.1.1.2 For samples whose dissolution is hastened by HF, add 8 mL to 10 mL of HCl (1 + 1), and heat. Add HNO and a few
drops of HF as needed to hasten dissolution, and then add 3 mL to 4 mL of HNO . When dissolution is complete, cool, then add
10 mL of HClO , evaporate to fumes to oxidize chromium, if present, and to expel HCl. Continue fuming until salts begin to
separate. Cool, add 50 mL of water, digest if necessary to dissolve the salts, cool, and transfer the solution to either a 100-mL or
500-mL volumetric flask as indicated in 16.1. Proceed to 16.1.3.
16.1.2 For Samples Containing More Than 0.5 % Tungsten:
16.1.2.1 To dissolve samples that do not require HF, add 8 mL to 10 mL of H PO , 10 mL of HClO , 5 mL to 6 mL of H SO ,
3 4 4 2 4
and 3 mL to 4 mL of HNO . Heat moderately until the sample is decomposed, and then heat to copious white fumes for 10 min
to 12 min or until the chromium is oxidized and the HCl is expelled, but avoid heating to fumes of SO . Cool, add 50 mL of water,
and digest, if necessary, to dissolve the salts. Transfer the solution to either a 100-mL or 500-mL volumetric flask as directed in
16.1. Proceed to 16.1.3.
16.1.2.2 For samples whose dissolution is hastened by HF, add 8 mL to 10 mL of H PO , 10 mL of HClO , 5 mL to 6 mL of
3 4 4
H SO , 3 mL to 4 mL of HNO , and a few drops of HF. Heat moderately until the sample is decomposed, and then heat to copious
2 4 3
white fumes for 10 min to 12 min or until the chromium is oxidized and the HCl is expelled, but avoid heating to fumes of SO .
Cool, add 50 mL of water, digest, if necessary, to dissolve the salts, cool, and transfer the solution to either a 100-mL or 500-mL
volumetric flask as directed in 16.1. Proceed to 16.1.3.
16.1.3 Cool the solution to room temperature, dilute to volume, and mix. Allow insoluble matter to settle, or dry-filter through a
coarse paper and discard the first 15 mL to 20 mL of the filtrate, before taking aliquots.
16.1.4 Using a pipet, transfer 10 mL to 20 mL aliquots, as specified in 16.1 to two 50-mL borosilicate glass volumetric flasks. Treat
one portion as directed in 16.3. Treat the other portion as directed in 16.4.1.
16.2 Reagent Blank Solution—Carry a reagent blank through the entire procedure using the same amounts of all reagents with the
sample omitted.
16.3 Color Development—Proceed as directed in 15.3.
16.4 Reference Solutions:
16.4.1 Background Color Solution—To one of the sample aliquots in a 50-mL volumetric flask, add 10 mL of nitric-phosphoric
acid mixture, and heat the solution at not less than 90 °C for 20 min to 30 min (Note 2). Cool, dilute to volume (with untreated
water), and mix.
16.4.2 Reagent Blank Reference Solution—Transfer the reagent blank solution (16.2) to the same size volumetric flask as used for
the test solutions and transfer the same size aliquots as used for the test solutions to two 50-mL volumetric flasks. Treat one portion
as directed in 16.3 and use as reference solution for test samples. Treat the other as directed in 16.4.1 and use as reference solution
for Background Color Solutions.
16.5 Spectrophotometry—Establish the cell corrections with the Reagent Blank Reference solution to be used as a reference
solution for Background Color solutions. Take the spectrophotometric absorbance readings of the Background Color Solutions and
the test solutions versus the respective Reagent Blank Reference Solutions as directed in 15.4.
E352 − 23
TABLE 1 Statistical Information—Manganese by the
Metaperiodate Spectrophotometric Method
Man- Repeata- Repro-
ganese bility ducibil-
Test Specimen
Found, (R , ity (R ,
1 2
% E173) E173)
1. Special W high-speed tool 0.160 0.012 0.035
steel (NIST 440, 0.15
Mn)
2. Tool steel (NIST 153a, 0.183 0.005 0.010
0.192 Mn)
3. W high-speed tool steel 0.268 0.010 0.034
(NIST 441, 0.27 Mn)
4. Alloy Steel (NIST, 159, 0.819 0.010 0.034
a, 0.807 Mn)
5. Low Alloy Steel (NIST 1.91 0.02 0.04
100b, 1.89 Mn)
6. Stainless Steel (NIST 444, 4.60 0.04 0.13
4.62 Mn)
17. Calculation
17.1 Convert the net spectrophotometric absorbance reading of the test solution and of the background color solution to milligrams
of manganese by means of the calibration curve. Calculate the percentage of manganese as follows:
Manganese, %5 A 2 B / C ×10 (1)
~ ! ~ !
where:
A = manganese, mg, found in 50 mL of the final test solution,
B = apparent manganese, mg, found in 50 mL of the final background color solution, and
C = sample mass, g, represented in 50 mL of the final test solution.
18. Precision and Bias
18.1 Precision—Nine laboratories cooperated in testing this method and obtained the data summarized in Table 1.
18.2 Bias—The accuracy of this test method has been deemed satisfactory based upon the data for the certified reference materials
in Table 1. Users are encouraged to use these or similar reference materials to verify that the test method is performing accurately
in their laboratories.
PHOSPHORUS BY THE MOLYBDENUM BLUE SPECTROPHOTOMETRIC METHOD
19. Scope
19.1 This test method covers the determination of phosphorus from 0.002 % to 0.05 %.
20. Summary of Method
20.1 The sample is dissolved in mixed acids and the solution is fumed with HClO . Ammonium molybdate is added to react with
the phosphorus to form the heteropoly phosphomolybdate. This species is then reduced with hydrazine sulfate to form the
molybdenum blue complex. Spectrophotometric absorbance measurement is made at 650 nm or 825 nm, depending upon the
concentration.
21. Concentration Range
21.1 The recommended concentration range is from 0.005 mg to 0.05 mg of phosphorus per 100 mL of solution when measured
at 825 nm and from 0.05 mg to 0.3 mg of phosphorus per 100 mL of solution when measured at 650 nm, using a 1-cm cell.
NOTE 3—This test method has been written for cells having a 1-cm light path. Cells having other dimensions may be used, provided suitable adjustments
can be made in the amounts of sample and reagents used.
E352 − 23
22. Stability of Color
22.1 The molybdenum blue complex is stable for at least 2 h.
23. Interferences
23.1 None of the elements usually present interfere except arsenic which is removed by volatilization as the bromide. The
interference of tungsten at compositions greater than 0.5 % is avoided by proceeding directly with a small sample mass rather than
an aliquot portion of a larger sample.
24. Apparatus
24.1 Glassware must be phosphorus- and arsenic-free. Boil the glassware with HCl and rinse with water before use. It is
recommended that the glassware used for this determination be reserved for this use only. Many detergents contain phosphorus
and must not be used for cleaning purposes.
25. Reagents
25.1 Ammonium Molybdate Solution (20 g/L)—Cautiously, while stirring and cooling, add 300 mL of H SO to 500 mL of water
2 4
and cool. Add 20 g of ammonium heptamolybdate ((NH ) Mo O ·4H O), cautiously dilute to 1 L, and mix.
4 6 7 24 2
25.2 Ammonium Molybdate-Hydrazine Sulfate Solution—Dilute 250 mL of the ammonium molybdate solution to 600 mL, add 100
mL of the hydrazine sulfate solution, dilute to 1 L, and mix. Do not use a solution that has stood for more than 1 h.
25.3 Hydrazine Sulfate Solution (1.5 g/L)—Dissolve 1.5 g of hydrazine sulfate ((NH ) ·H SO ) in water, dilute to 1 L, and mix.
2 2 2 4
Discard any unused solution after 24 h.
25.4 Phosphorus Standard Solution A (1 mL = 1.0 mg P)—Transfer 2.292 g of anhydrous disodium hydrogen phosphate
(Na HPO ), previously dried to constant mass at 105 °C, to a 500-mL volumetric flask; dissolve in about 100 mL of water, dilute
2 4
to volume, and mix.
25.5 Phosphorus Standard Solution B (1 mL = 0.01 mg P)—Using a pipet, transfer 10 mL of Solution A (1 mL = 1.0 mg P) to
a 1-L volumetric flask, add 50 mL of HClO (1 + 5), dilute to volume, and mix.
25.6 Phosphorus Standard Solution C (1 mL = 0.10 mg P)—Using a pipet, transfer 50 mL of Solution A (1 mL = 1.0 mg P) to
a 500-mL volumetric flask, add 50 mL of HClO (1 + 5), dilute to volume, and mix.
25.7 Sodium Sulfite Solution (100 g/L)—Dissolve 100 g of sodium sulfite (Na SO ) in water, dilute to 1 L, and mix.
2 3
26. Preparation of Calibration Curve for Concentrations from 0.005 mg/100 mL to 0.05 mg/100 mL
26.1 Calibration Solutions—Using pipets, transfer 5 mL, 10 mL, 15 mL, 25 mL, and 50 mL of Phosphorus Standard Solution B
(1 mL = 0.01 mg P) to 100-mL volumetric flasks. Add 20 mL of HClO , dilute to volume, and mix. Using a pipet, transfer 10 mL
of each solution to a 100-mL borosilicate glass volumetric flask. Proceed as directed in 26.3.
26.2 Reagent Blank—Transfer 12 mL of HClO (1 + 5) to a 100-mL borosilicate glass volumetric flask.
26.3 Color Development:
26.3.1 Add 15 mL of Na SO solution, boil gently for 30 s, and add 50 mL of ammonium molybdate-hydrazine sulfate solution
2 3
that has been prepared within the hour.
26.3.2 Heat the solutions at not less than 90 °C for 20 min, quickly cool, dilute to volume, and mix.
NOTE 4—Immersing the flasks in a boiling water bath is the preferred means of heating them for complete color development.
E352 − 23
26.4 Reference Solution—Water.
26.5 Spectrophotometry:
26.5.1 Multiple-Cell Spectrophotometer—Measure the reagent blank (which includes the cell correction) versus the reference
solution (26.4) using absorption cells with a 1-cm light path and using a light band centered at 825 nm. Using the test cell, take
the spectrophotometric absorbance readings of the calibration solutions versus the reference solution.
26.5.2 Single-Cell Spectrophotometer—Transfer a suitable portion of the reference solution (26.4) to an absorption cell with a
1-cm light path and adjust the spectrophotometer to the initial setting using a light band centered at 825 nm. While maintaining
this adjustment, take the spectrophotometric absorbance readings of the reagent blank solution and of the calibration solutions.
26.6 Calibration Curve—Follow the instrument manufacturer’s instructions for generating the calibration curve. Plot the net
spectrophotometric absorbance readings of the calibration solutions against the milligrams of phosphorus per 100 mL of solution.
27. Procedure
27.1 For Samples Containing Less Than 0.5 % Tungsten:
27.1.1 Test Solution:
27.1.1.1 Transfer a 1.0-g sample, weighed to the nearest 0.5 mg, to a 250-mL Erlenmeyer flask.
27.1.1.2 Add 15 mL of a freshly prepared mixture of 1 volume of HNO and 3 volumes of HCl, slowly and in small portions.
When the reaction has ceased, add 10 mL of HClO and evaporate to fumes. Remove the flask immediately to avoid undue loss
of HClO , cool, and add 20 mL of HBr (1 + 4). Evaporate the solution to copious white fumes and then, without delay, fume
strongly enough to cause the white fumes to clear the neck of the flask, and continue at this rate for 1 min.
27.1.1.3 Cool the solution, add 60 mL of HClO (1 + 5), and swirl to dissolve the salts. Transfer to a 100-mL volumetric flask,
cool, dilute to volume, and mix. Allow insoluble matter to settle or dry filter the solution. Using a pipet, transfer 10-mL portions
to two 100-mL borosilicate glass volumetric flasks; treat one as directed in 27.1.3 and the other as directed in 27.1.4.2.
27.1.2 Reagent Blank Solution—Carry a reagent blank through the entire procedure using the same amount of all reagents with
the sample omitted.
27.1.3 Color Development—Proceed with one of the 10-mL portions obtained in 27.1.1.3, as directed in 26.3.
27.1.4 Reference Solutions:
27.1.4.1 Water—Use this as the reference solution for the reagent blank solution.
27.1.4.2 Background Color Reference Solution—Add 15 mL of Na SO solution to the second 10-mL portion obtained in 27.1.1.3.
2 3
Boil gently for 30 s, add 50 mL of H SO (3 + 37), cool, dilute to volume, and mix. Use this as the reference solution for the test
2 4
solution.
27.1.5 Spectrophotometry—Take the spectrophotometric absorbance readings of the reagent blank solution and of the test solution
(using the respective reference solutions) as directed in 26.5.
27.2 For Samples Containing More Than 0.5 % Tungsten:
27.2.1 Test Solution:
27.2.1.1 Transfer 0.100-g samples, weighed to the nearest 0.1 mg, to two 100-mL Erlenmeyer flasks.
27.2.1.2 Add 5 mL of a mixture of 1 volume of HNO and 3 volumes of HCl. When the reaction has ceased, add 2.5 mL of HClO
3 4
E352 − 23
and 5 mL of HBr (1 + 4). Evaporate the solutions to copious white fumes; then, without delay, fume strongly enough to cause the
white fumes to clear the neck of the flasks, and continue at this rate for 1 min.
27.2.1.3 Cool the solutions, and add 10 mL of water. Filter through a 9-cm fine paper collecting the filtrate in a 100-mL
borosilicate glass volumetric flask. Wash the paper and insoluble matter 5 times with 3-mL portions of water. Treat one solution
as directed in 27.2.3 and the other as directed in 27.2.4.
27.2.2 Reagent Blank Solution—Proceed as directed in 27.2.1.2 and 27.2.1.3.
27.2.3 Color Development—Proceed as directed in 26.3.
27.2.4 Reference Solutions:
27.2.4.1 Water—Use this as the reference solution for the reagent blank solution.
27.2.4.2 Background Color Reference Solution—Add 15 mL of Na SO solution to the second 10-mL portion obtained in 27.2.1.3.
2 3
Boil gently for 30 s, add 50 mL of H SO (3 + 37), cool, dilute to volume, and mix. Use this as the reference solution for the test
2 4
solution.
27.2.5 Spectrophotometry—Proceed as directed in 27.1.5.
28. Calculation
28.1 Convert the net spectrophotometric absorbance reading of the test solution and of the reagent blank solution to milligrams
of phosphorus by means of the appropriate calibration curve. Calculate the percent of phosphorus as follows:
Phosphorus,%5 A 2 B ⁄ C × 10 (2)
~ ! ~ !
where:
A = phosphorus found in 100 mL of the final test solution, mg,
B = phosphorus found in 100 mL of the final reagent blank solution, mg, and
C = sample represented in 100 mL of the final test solution, g.
29. Precision and Bias
29.1 Precision—Eight laboratories cooperated in testing this method and obtained the data summarized in Table 2.
29.2 Bias—The accuracy of this test method has been deemed satisfactory based upon the data for the certified reference materials
in Table 2. Users are encouraged to use these or similar reference materials to verify that the test method is performing accurately
in their laboratories.
TABLE 2 Statistical Information—Phosphorus – Molybdenum
Blue – Spectrophotometric Method
Phos- Repeata- Repro-
phorus bility ducibil-
Test Specimen
Found, (R , ity (R ,
1 2
% E173) E173)
1. Tool steel 5Mo-6W-4Cr-2V 0.029 0.011 0.008
(NIST 132a, 0.029 P)
2. Tool steel 8Co-9Mo-2W- 0.023 0.008 0.007
4Cr-2V (NIST 153a,
0.023 P)
3. Tool steel 18W-4Cr-1V 0.022 0.005 0.007
(NIST 50c, 0.022 P)
E352 − 23
SULFUR BY THE GRAVIMETRIC METHOD
(This method, which consisted of Sections 29 through 35 of this standard, was discontinued in 1988.)
SULFUR BY THE COMBUSTION-IODATE TITRATION METHOD
(This method, which consisted of Sections 36 through 44 of this standard, was discontinued in 2012.)
SILICON BY THE GRAVIMETRIC METHOD
45. Scope
45.1 This method covers the determination of silicon from 0.10 % to 2.50 %.
46. Summary of Method
46.1 After dissolution of the sample, silicic acid is dehydrated by fuming with H SO or HClO . The solution is filtered, and the
2 4 4
impure silica is ignited and weighed. The silica is then volatilized with HF. The residue is ignited and weighed; the loss in mass
represents silica.
47. Interferences
47.1 The elements normally present do not interfere if their compositions are under the maximum limits shown in 1.1.
48. Reagents
48.1 The analyst should ensure by analyzing blanks and other checks that possible silicon contamination of reagents will not
significantly bias the results.
48.2 Perchloric Acid (HClO ):
48.2.1 Select a lot of HClO that contains not more than 0.0002 % silicon for the analysis of samples containing silicon in the
range from 0.02 % to 0.10 % and not more than 0.0004 % silicon for samples containing more than 0.10 % by determining
duplicate values for silicon as directed in 48.2.2 – 48.2.6.
48.2.2 Transfer 15 mL of HClO (Note 5) to each of two 400-mL beakers. To one of the beakers transfer an additional 50 mL of
HClO . Using a pipet, transfer 20 mL of Na SiO solution (1 mL = 1.00 mg Si) to each of the beakers. Evaporate the solutions
4 2 3
to fumes and heat for 15 min to 20 min at such a rate that HClO refluxes on the sides of the beakers. Cool sufficiently, and add
100 mL of water (40 °C to 50 °C).
NOTE 5—The 15-mL addition of HClO can be from the same lot as the one to be tested. Once a lot has been established as having less than 0.0002 %
silicon, it should preferably be used for the 15-mL addition in all subsequent tests of other lots of acid.
48.2.3 Add paper pulp and filter immediately, using low-ash 11-cm medium-porosity filter papers. Transfer the precipitates to the
papers, and scrub the beakers thoroughly with a rubber-tipped rod. Wash the papers and precipitates alternately with 3 mL to 5
mL portions of hot HCl (1 + 19) and hot water, for a total of 6 times. Finally wash the papers twice with H SO (1 + 49). Transfer
2 4
the papers to platinum crucibles.
48.2.4 Dry the papers and heat at 600 °C until the carbon is removed. Finally ignite at 1100 °C to 1150 °C to constant mass (at
least 30 min). Cool in a desiccator and weigh.
48.2.5 Add enough H SO (1 + 1) to moisten the SiO , and add 3 mL to 5 mL of HF. Evaporate to dryness and then heat at a
2 4 2
gradually increasing rate until H SO is removed. Ignite for 15 min at 1100 °C to 1150 °C, cool in a desiccator, and weigh.
2 4
E352 − 23
48.2.6 Calculate the percent of silicon as follows:
Silicon,%5 A 2 B 2 C 2 D ×0.4674⁄E ×100 (3)
@~ ! ~ !#
where:
A = initial mass of crucible plus impure SiO when 65 mL of HClO was taken, g,
2 4
B = final mass of crucible plus impurities when 65 mL of HClO was taken, g,
C = initial mass of crucible plus impure SiO when 15 mL of HClO was taken, g,
2 4
D = final mass of crucible plus impurities when 15 mL of HClO was taken, g, and
E = nominal mass (80 g) of 50 mL of HClO .
48.3 Sodium Silicate Solution—Transfer 11.0 g of sodium silicate (Na SiO ·9H O) to a 400-mL beaker. Add 150 mL of water and
2 3 2
dissolve the salt. Filter through a medium paper, collecting the filtrate in a 1-L volumetric flask, dilute to volume, and mix. Store
in a polyethylene bottle. Use this solution to determine the suitability of the HClO .
48.4 Tartaric Acid Solution (20.6 g/L)—Dissolve 20.6 g of tartaric acid (C H O ) in water, dilute to 1 L, and filter.
4 6 6
48.5 Water—Use freshly prepared Type II water known to be free of silicon. Water distilled from glass, demineralized in columns
containing silicon compounds, or stored for extended periods in glass, or combination thereof, has been known to absorb silicon.
49. Procedure
49.1 Select and weigh a sample as follows:
Dehydrating Acid, mL
Tolerance in
Sample Sample H SO
2 4
Silicon, % Mass, g Mass, mg (1 + 4) HClO
0.1 to 0.1 4.0 4 150 60
1.0 to 1.75 3.0 3 100 50
1.75 to 2.50 2.0 2 100 40
Transfer it to a 400-mL beaker or a 300-mL porcelain casserole. Proceed as directed in 49.2 if tungsten is greater than 0.5% or
if tungsten is less than 0.5%, proceed as directed in 49.2 or 49.3.
49.2 Sulfuric Acid Dehydration (H SO ):
2 4
49.2.1 Add amounts of HCl or HNO , or mixtures and dilutions of these acids, that are sufficient to dissolve the sample; and then
add the H SO (1 + 4) as specified in 49.1, and cover. Heat until dissolution is complete. Remove and rinse the cover glass;
2 4
substitute a ribbed cover glass.
49.2.2 Evaporate until salts begin to separate; at this point evaporate the solution rapidly to the first appearance of fumes and fume
strongly for 2 min to 3 min. Cool sufficiently, and add 100 mL of water (40 °C to 50 °C). Stir to dissolve the salts and heat, if
necessary, but do not boil. Proceed immediately as directed in 49.4.
49.3 Perchloric Acid (HClO ) Dehydration:
49.3.1 Add amounts of HCl or HNO , or mixtures and dilutions of these acids, which are sufficient to dissolve the sample, and
cover. Heat until dissolution is complete. Add HNO to provide a total of 35 mL to 40 mL, followed by HClO as specified in the
3 4
table in 49.1. Remove and rinse the cover glass; substitute a ribbed cover glass.
49.3.2 Evaporate the solution to fumes and heat for 15 min to 20 min at such a rate that the HClO refluxes on the sides of the
container. Cool sufficiently and add 100 mL of water (40 °C to 50 °C). Stir to dissolve the salts and heat to boiling. If the sample
solution contains more than 100 mg of chromium, add, while stirring, 1 mL of tartaric acid solution for each 25 mg of chromium.
49.4 Add paper pulp and filter immediately, on a low-ash 11-cm medium-porosity filter paper. Collect the filtrate in a 600-mL
beaker. Transfer the precipitate to the paper, and scrub the container thoroughly with a rubber-tipped rod. Wash the paper and
precipitate alternately with 3 mL to 5 mL portions of hot HCl (1 + 19) and hot water until iron salts are removed but for not more
E352 − 23
than a total of ten washings. If the HClO dehydration method was followed, wash the paper twice more with H SO (1 + 49),
4 2 4
but do not collect these washings in the filtrate; discard the washings. Transfer the paper to a platinum crucible and reserve.
49.5 Add 15 mL of HNO to the filtrate, stir, and evaporate in accordance with either 49.2 or 49.3, depending upon the dehydrating
acid used. Filter immediately, using a low-ash, 9-cm 100-porosity filter paper, and wash as directed in 49.4.
49.6 Transfer the paper and precipitate to the reserved platinum crucible. Dry the papers and then heat the crucible at 600 °C until
the carbon is removed. Finally ignite at 1100 °C to 1150 °C to constant mass (at least 30 min). Cool in a desiccator and weigh.
49.7 Add enough H SO (1 + 1) to moisten the impure SiO , and add 3 mL to 5 mL of HF. Evaporate to dryness and then heat
2 4 2
at a gradually increasing rate until H SO is removed. Ignite at 1100 °C to 1150 °C for 15 min, cool in a desiccator, and weigh.
2 4
If the sample contains more than 0.5 % tungsten, ignite at 750 °C instead of 1100 °C to 1150 °C after volatilization of SiO .
50. Calculation
50.1 Calculate the percent of silicon as follows:
Silicon,%5 @~~A 2 B! ×0.4674!⁄C# ×100 (4)
where:
A = initial mass of crucible and impure SiO , g,
B = final mass of crucible and residue, g, and
C = sample used, g.
51. Precision and Bias
51.1 Precision—Eleven laboratories cooperated in testing this method and obtained the data summarized in Table 3. Samples with
tungsten below 0.5 % were not available for testing the HClO dehydration procedure; neither were samples available with
tungsten greater than 0.5 % for testing the H SO dehydration procedure near the upper limit of the scope.
2 4
51.2 Bias—Either this method has no bias, or this method is subject to bias under certain sample conditions. Only one certified
reference material was available for testing during the interlaboratory study, see Table 3. The user of this method is encouraged
to utilize accepted reference materials, if available, to determine the presence or absence of bias.
COBALT BY THE ION-EXCHANGE—POTENTIOMETRIC TITRATION METHOD
52. Scope
52.1 This method covers the determination of cobalt from
2 % to 14 %.
53. Summary of Method
53.1 Cobalt is separated from interfering elements by selective elution from an anion-exchange column using HCl. The cobalt is
oxidized to the trivalent state with ferricyanide, and the excess ferricyanide is titrated potentiometrically with cobalt solution.
TABLE 3 Statistical Information—Silicon – Gravimetric Method
Silicon
Repeatability Reproducibility
Test Specimen Found,
(R , E173) (R , E173)
1 2
%
H SO Dehydration
2 4
1. Tool steel 5Mo-6W-4Cr-2V 0.193 0.019 0.031
(NIST 132a, 0.19 Si)
E352 − 23
54. Interferences
54.1 The elements normally present do not interfere if their compositions are under the maximum limits shown in 1.1.
55. Apparatus
55.1 Ion-Exchange Column, approximately 25 mm in diameter and 300 mm in length, tapered at one end, and provided with a
stopcock to control the flow rate, and a second, lower stopcock to stop the flow. A Jones Reductor (Fig. 1) may be adapted to this
method. A reservoir for the eluants may be added at the top of the column.
55.2 pH meter, with a platinum and a saturated calomel electrode.
56. Reagents
56.1 Ammonium Citrate Solution (200 g/l)—Dissolve 200 g of di–ammonium hydrogen citrate in water and dilute to 1 L.
56.2 Bromine
56.3 Cobalt, Standard Solution (1mL = 1.5 mg of Co):
56.3.1 Preparation—Dry a weighing bottle in an oven at 130 °C for 1 h, cool in a desiccator, and weigh. Transfer 3.945 g of cobalt
sulfate (CoSO ) that has been heated at 550 °C for 1 h to the weighing bottle. Dry the bottle and contents at 130 °C for 1 h, cool
in desiccator, stopper the bottle, and weigh. The difference in mass is the amount of CoSO taken. Transfer the weighed CoSO
4 4
to a 400-mL beaker, rinse the weighing bottle with water, and transfer the rinsings to the beaker. Add 150 mL of water and 20 mL
of HNO , and heat to dissolve the salts. Cool, transfer to a 1-L volumetric flask, dilute to volume, and mix.
56.3.2 Standardization—Calculate the cobalt concentration as follows:
Cobalt,mg⁄mL5 massofCoSO ,g ×0.38026 (5)
FIG. 1 Jones Reductor
Cobalt sulfate (99.9 % minimum) prepared from the hexamine salt by G. Frederick Smith Chemical Co., Columbus, OH, is satisfactory for this purpose.
E352 − 23
56.4 Ion-Exchange Resin:
56.4.1 Use an anion exchange resin of the alkyl quaternary ammonium type (chloride form) consisting of spherical beads having
a nominal crosslinkage of 8 %, and 0.075-mm to 0.037-mm (200-nominal to 400-nominal mesh) size. To remove those beads
greater than about 180-μm in diameter as well as the excessively fine beads, treat the resin as follows: Transfer a supply of the
resin to a beaker, cover with water, and allow sufficient time (at least 30 min) for the beads to undergo maximum swelling. Place
a 180-μm (No. 80) screen, 150 mm in diameter over a 2-L beaker. Prepare a thin slurry of the resin and pour it onto the screen.
Wash the fine beads through the screen, using a small stream of water. Discard the beads retained on the screen, periodically, if
necessary, to avoid undue clogging of the openings. When the bulk of the collected resin has settled, decant the water and transfer
approximately 100 mL of resin to a 400-mL beaker. Add 200 mL of HCl (1 + 19), stir vigorously, allow the resin to settle for 4
min to 6 min, decant 150 mL to 175 mL of the suspension, and discard. Repeat the treatment with HCl (1 + 19) twice more, and
reserve the coarser resin for the column preparation.
56.4.2 Prepare the column as follows: Place a 10-mm to 20-mm layer of glass wool or polyvinyl chloride plastic fiber in the
bottom of the column, and add a sufficient amount of the prepared resin to fill the column to a heigh
...

Questions, Comments and Discussion

Ask us and Technical Secretary will try to provide an answer. You can facilitate discussion about the standard in here.

Loading comments...