Standard Test Methods for Chemical Analysis of Cast Iron—All Types

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 A04 on Iron Castings. 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 pig iron, gray cast iron (including alloy and austenitic), white cast iron, malleable cast iron, and ductile (nodular) iron having chemical compositions within the following limits:    
Element  
Composition Range, %  
Aluminum  
0.003 to 0.50  
Antimony  
0.005 to 0.03  
Arsenic  
0.02 to 0.10  
Bismuth  
0.001 to 0.03  
Boron  
0.001 to 0.10  
Cadmium  
0.001 to 0.005  
Carbon  
1.25 to 4.50  
Cerium  
0.005 to 0.05  
Chromium  
0.01 to 30.00  
Cobalt  
0.01 to 4.50  
Copper  
0.03 to 7.50  
Lead  
0.001 to 0.15  
Magnesium  
0.002 to 0.10  
Manganese  
0.06 to 2.50  
Molybdenum  
0.01 to 5.00  
Nickel  
0.01 to 36.00  
Phosphorus  
0.01 to 0.90  
Selenium  
0.001 to 0.06  
Silicon  
0.10 to 6.0    
Sulfur  
0.005 to 0.25  
Tellurium  
0.001 to 0.35  
Tin  
0.001 to 0.35  
Titanium  
0.001 to 0.20  
Tungsten  
0.001 to 0.20  
Vanadium  
0.005 to 0.50  
Zinc  
0.005 to 0.20  
1.2 The test methods in this standard are contained in the sections indicated below:    
Sections  
Carbon, Graphitic, by the Direct Combustion Infrared Absorption Method (1 % to 3 %)  
108–115  
Carbon, Total by the Combustion Gravimetric Method (1.25 % to 4.50 %)—Discontinued 2012  
97–107  
Cerium and Lanthanum by the Direct Current Plasma Atomic Emission Spectrometry Method (Ce: 0.003 % to 0.5 %; La: 0.001 % to 0.30 %)  
237–245  
Chromium by the Atomic Absorption Method (0.006 % to 1.00 %)  
208–217  
Chromium by the Peroxydisulfate Oxidation—Titration Method (0.05 % to 30.0 %)  
218–226  
Chromium by the Peroxydisulfate-Oxidation Titrimetric Method (0.05 % to 30.0 %)—Discontinued 1980  
144–151    
Cobalt by the Ion-Exchange—Potentiometric Titration Method (2.0 % to 4.5 %)  
53–60  
Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.01 % to 4.50 %)  
61–70  
Copper by the Neocuproine Spectrophotometric Method (0.03 % to 7.5 %)  
116–125  
Copper by the Sulfide Precipitation-Electrodeposition Gravimetric Method (0.03 % to 7.5 %)  
81–88  
Lead by the Ion-Exchange—Atomic Absorption Spectrometry Method (0.001 % to 0.15 %)  
126–135  
Magnesium by the Atomic Absorption Spectrometry Method (0.002 % to 0.10 %)  
71–80  
Manganese by the Periodate Spectrophotometric Method (0.10 % to 2.00 %)  
9–18  
Manganese by the Peroxydisulfate-Arsenite Titrimetric Method (0.10 % to 3.5 %)  
152–159  
Molybdenum by the Ion Exchange–8-Hydroxyquinoline Gravimetric Method  
257–264  
Molybdenum by the Thiocyanate Spectrophotometric Method (0.01 % to 1.5 %)  
196–207  
Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 36.00 %)  
168–175  
Nickel by the Ion Exchange-Atomic Absorption Spectrometry Method (0.005 % to 1.00 %)  
176–185  
Phosphorus by the Alkalimetric Method (0.02 % to 0.90 %)  
160–167  
Phosphorus by the Molybdenum Blue Spectrophotometric Method (0.02 % to 0.90 %)  
19–30  
Silicon by the Gravimetric Method (0.1 % to 6.0 %)  
46–52  
Sulfur by the Gravimetric Method—Discontinued 1988  
30–36  
Sulfur by the Combustion-Iodate Titration Method (0.005 % to 0.25 %)—Discontinued 2012  
37–45  
Sulfur by the Chromatographic Gravimetric Method—Discontinued 1980  
136–143    
Tin by the Solvent Extraction-A...

General Information

Status
Published
Publication Date
30-Jun-2018

Relations

Effective Date
01-Jul-2018
Effective Date
15-Nov-2023
Effective Date
15-Nov-2023
Effective Date
01-Jan-2020
Effective Date
01-Nov-2019
Effective Date
15-May-2019
Effective Date
01-Sep-2017
Effective Date
01-Dec-2016
Effective Date
01-Dec-2016
Effective Date
01-Aug-2016
Effective Date
15-May-2016
Effective Date
01-Jul-2015
Effective Date
15-May-2015
Effective Date
15-Sep-2014
Effective Date
15-Aug-2014

Overview

ASTM E351-18 – Standard Test Methods for Chemical Analysis of Cast Iron-All Types establishes referee test methods for determining the chemical composition of various types of cast iron. These methods are widely recognized for analyzing pig iron, gray cast iron (including alloy and austenitic types), white cast iron, malleable cast iron, and ductile (nodular) iron. The standard specifies compositional ranges for multiple elements commonly present in iron castings, ensuring that analyses meet product specifications, particularly under the jurisdiction of ASTM Committee A04 on Iron Castings.

Designed for use by skilled analysts in properly equipped laboratories, the standard supports compliance with chemical composition requirements and is intended as a reference for quality control processes in the iron foundry and metallurgy industries.

Key Topics

ASTM E351-18 covers a broad spectrum of analytical methods and chemical elements found in cast iron materials. Key topics include:

  • Elemental Composition Analysis: Methods for determining the concentrations of elements such as:
    • Aluminum, Antimony, Arsenic, Bismuth, Boron, Cadmium, Carbon, Cerium, Chromium, Cobalt, Copper, Lead, Magnesium, Manganese, Molybdenum, Nickel, Phosphorus, Selenium, Silicon, Sulfur, Tellurium, Tin, Titanium, Tungsten, Vanadium, and Zinc.
  • Analytical Techniques: These include:
    • Direct combustion infrared absorption
    • Atomic absorption spectrometry
    • Spectrophotometry
    • Ion-exchange methods
    • Gravimetric and titrimetric analysis
  • Selection of Appropriate Methods: Multiple techniques are often provided for the same element to accommodate wide concentration ranges and potential spectral or matrix interferences.
  • Quality Control and Safety: The standard expects laboratories to adhere to robust quality control procedures (for example, those outlined in ASTM E882) and to maintain high safety standards.

Applications

ASTM E351-18 is integral to the iron and steel industry, particularly for those involved in:

  • Metal Production and Foundries: Ensuring pig iron and cast iron products meet strict compositional specifications.
  • Material Qualification and Certification: Supporting product conformance for critical infrastructure, automotive, and machinery components.
  • Research and Development: Providing a consistent analytical basis when developing new alloys or improving manufacturing processes.
  • Quality Assurance: Serving as a benchmark in interlaboratory comparisons and for validating new analytical procedures.

The use of standardized chemical analysis methods in this document is essential for manufacturers, laboratories, suppliers, and purchasers of cast iron materials to verify product quality, reduce variance, and facilitate trade.

Related Standards

Professionals utilizing ASTM E351-18 may also reference the following related standards to ensure comprehensive chemical analysis and laboratory practice in metals:

  • ASTM 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
  • ASTM E882: Guide for Accountability and Quality Control in the Chemical Analysis Laboratory
  • ASTM E29: Practice for Using Significant Digits in Test Data to Determine Conformance with Specifications
  • ASTM E1806: Practice for Sampling Steel and Iron for Determination of Chemical Composition
  • ASTM E50: Practices for Apparatus, Reagents, and Safety Considerations for Chemical Analysis of Metals, Ores, and Related Materials

By following ASTM E351-18 and related standards, organizations can achieve reliable, reproducible results in the chemical analysis of cast iron, fostering confidence in material quality and regulatory compliance.

Buy Documents

Standard

ASTM E351-18 - Standard Test Methods for Chemical Analysis of Cast Iron—All Types

English language (57 pages)
sale 15% off
sale 15% off
Standard

REDLINE ASTM E351-18 - Standard Test Methods for Chemical Analysis of Cast Iron—All Types

English language (57 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 E351-18 is a standard published by ASTM International. Its full title is "Standard Test Methods for Chemical Analysis of Cast Iron—All Types". 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 A04 on Iron Castings. 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 pig iron, gray cast iron (including alloy and austenitic), white cast iron, malleable cast iron, and ductile (nodular) iron having chemical compositions within the following limits: Element Composition Range, % Aluminum 0.003 to 0.50 Antimony 0.005 to 0.03 Arsenic 0.02 to 0.10 Bismuth 0.001 to 0.03 Boron 0.001 to 0.10 Cadmium 0.001 to 0.005 Carbon 1.25 to 4.50 Cerium 0.005 to 0.05 Chromium 0.01 to 30.00 Cobalt 0.01 to 4.50 Copper 0.03 to 7.50 Lead 0.001 to 0.15 Magnesium 0.002 to 0.10 Manganese 0.06 to 2.50 Molybdenum 0.01 to 5.00 Nickel 0.01 to 36.00 Phosphorus 0.01 to 0.90 Selenium 0.001 to 0.06 Silicon 0.10 to 6.0 Sulfur 0.005 to 0.25 Tellurium 0.001 to 0.35 Tin 0.001 to 0.35 Titanium 0.001 to 0.20 Tungsten 0.001 to 0.20 Vanadium 0.005 to 0.50 Zinc 0.005 to 0.20 1.2 The test methods in this standard are contained in the sections indicated below: Sections Carbon, Graphitic, by the Direct Combustion Infrared Absorption Method (1 % to 3 %) 108–115 Carbon, Total by the Combustion Gravimetric Method (1.25 % to 4.50 %)—Discontinued 2012 97–107 Cerium and Lanthanum by the Direct Current Plasma Atomic Emission Spectrometry Method (Ce: 0.003 % to 0.5 %; La: 0.001 % to 0.30 %) 237–245 Chromium by the Atomic Absorption Method (0.006 % to 1.00 %) 208–217 Chromium by the Peroxydisulfate Oxidation—Titration Method (0.05 % to 30.0 %) 218–226 Chromium by the Peroxydisulfate-Oxidation Titrimetric Method (0.05 % to 30.0 %)—Discontinued 1980 144–151 Cobalt by the Ion-Exchange—Potentiometric Titration Method (2.0 % to 4.5 %) 53–60 Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.01 % to 4.50 %) 61–70 Copper by the Neocuproine Spectrophotometric Method (0.03 % to 7.5 %) 116–125 Copper by the Sulfide Precipitation-Electrodeposition Gravimetric Method (0.03 % to 7.5 %) 81–88 Lead by the Ion-Exchange—Atomic Absorption Spectrometry Method (0.001 % to 0.15 %) 126–135 Magnesium by the Atomic Absorption Spectrometry Method (0.002 % to 0.10 %) 71–80 Manganese by the Periodate Spectrophotometric Method (0.10 % to 2.00 %) 9–18 Manganese by the Peroxydisulfate-Arsenite Titrimetric Method (0.10 % to 3.5 %) 152–159 Molybdenum by the Ion Exchange–8-Hydroxyquinoline Gravimetric Method 257–264 Molybdenum by the Thiocyanate Spectrophotometric Method (0.01 % to 1.5 %) 196–207 Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 36.00 %) 168–175 Nickel by the Ion Exchange-Atomic Absorption Spectrometry Method (0.005 % to 1.00 %) 176–185 Phosphorus by the Alkalimetric Method (0.02 % to 0.90 %) 160–167 Phosphorus by the Molybdenum Blue Spectrophotometric Method (0.02 % to 0.90 %) 19–30 Silicon by the Gravimetric Method (0.1 % to 6.0 %) 46–52 Sulfur by the Gravimetric Method—Discontinued 1988 30–36 Sulfur by the Combustion-Iodate Titration Method (0.005 % to 0.25 %)—Discontinued 2012 37–45 Sulfur by the Chromatographic Gravimetric Method—Discontinued 1980 136–143 Tin by the Solvent Extraction-A...

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 A04 on Iron Castings. 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 pig iron, gray cast iron (including alloy and austenitic), white cast iron, malleable cast iron, and ductile (nodular) iron having chemical compositions within the following limits: Element Composition Range, % Aluminum 0.003 to 0.50 Antimony 0.005 to 0.03 Arsenic 0.02 to 0.10 Bismuth 0.001 to 0.03 Boron 0.001 to 0.10 Cadmium 0.001 to 0.005 Carbon 1.25 to 4.50 Cerium 0.005 to 0.05 Chromium 0.01 to 30.00 Cobalt 0.01 to 4.50 Copper 0.03 to 7.50 Lead 0.001 to 0.15 Magnesium 0.002 to 0.10 Manganese 0.06 to 2.50 Molybdenum 0.01 to 5.00 Nickel 0.01 to 36.00 Phosphorus 0.01 to 0.90 Selenium 0.001 to 0.06 Silicon 0.10 to 6.0 Sulfur 0.005 to 0.25 Tellurium 0.001 to 0.35 Tin 0.001 to 0.35 Titanium 0.001 to 0.20 Tungsten 0.001 to 0.20 Vanadium 0.005 to 0.50 Zinc 0.005 to 0.20 1.2 The test methods in this standard are contained in the sections indicated below: Sections Carbon, Graphitic, by the Direct Combustion Infrared Absorption Method (1 % to 3 %) 108–115 Carbon, Total by the Combustion Gravimetric Method (1.25 % to 4.50 %)—Discontinued 2012 97–107 Cerium and Lanthanum by the Direct Current Plasma Atomic Emission Spectrometry Method (Ce: 0.003 % to 0.5 %; La: 0.001 % to 0.30 %) 237–245 Chromium by the Atomic Absorption Method (0.006 % to 1.00 %) 208–217 Chromium by the Peroxydisulfate Oxidation—Titration Method (0.05 % to 30.0 %) 218–226 Chromium by the Peroxydisulfate-Oxidation Titrimetric Method (0.05 % to 30.0 %)—Discontinued 1980 144–151 Cobalt by the Ion-Exchange—Potentiometric Titration Method (2.0 % to 4.5 %) 53–60 Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.01 % to 4.50 %) 61–70 Copper by the Neocuproine Spectrophotometric Method (0.03 % to 7.5 %) 116–125 Copper by the Sulfide Precipitation-Electrodeposition Gravimetric Method (0.03 % to 7.5 %) 81–88 Lead by the Ion-Exchange—Atomic Absorption Spectrometry Method (0.001 % to 0.15 %) 126–135 Magnesium by the Atomic Absorption Spectrometry Method (0.002 % to 0.10 %) 71–80 Manganese by the Periodate Spectrophotometric Method (0.10 % to 2.00 %) 9–18 Manganese by the Peroxydisulfate-Arsenite Titrimetric Method (0.10 % to 3.5 %) 152–159 Molybdenum by the Ion Exchange–8-Hydroxyquinoline Gravimetric Method 257–264 Molybdenum by the Thiocyanate Spectrophotometric Method (0.01 % to 1.5 %) 196–207 Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 36.00 %) 168–175 Nickel by the Ion Exchange-Atomic Absorption Spectrometry Method (0.005 % to 1.00 %) 176–185 Phosphorus by the Alkalimetric Method (0.02 % to 0.90 %) 160–167 Phosphorus by the Molybdenum Blue Spectrophotometric Method (0.02 % to 0.90 %) 19–30 Silicon by the Gravimetric Method (0.1 % to 6.0 %) 46–52 Sulfur by the Gravimetric Method—Discontinued 1988 30–36 Sulfur by the Combustion-Iodate Titration Method (0.005 % to 0.25 %)—Discontinued 2012 37–45 Sulfur by the Chromatographic Gravimetric Method—Discontinued 1980 136–143 Tin by the Solvent Extraction-A...

ASTM E351-18 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 E351-18 has the following relationships with other standards: It is inter standard links to ASTM E351-13, ASTM E352-23, ASTM E350-23, ASTM E135-20, ASTM E1601-19, ASTM E135-19, ASTM E50-17, ASTM E882-10(2016), ASTM E882-10(2016)e1, ASTM E50-11(2016), ASTM E135-16, ASTM E135-15a, ASTM E135-15, ASTM E353-14, ASTM E135-14b. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM E351-18 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: E351 − 18
Standard Test Methods for
Chemical Analysis of Cast Iron—All Types
This standard is issued under the fixed designation E351; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision.Anumber in parentheses indicates the year of last reapproval.A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
This standard has been approved for use by agencies of the U.S. Department of Defense.
1. Scope
Cerium and Lanthanum by the Direct Current Plasma Atomic
Emission Spectrometry Method (Ce: 0.003 % to 0.5 %; La: 0.001
1.1 These test methods cover the chemical analysis of pig
% to 0.30 %) 237–245
Chromium by the Atomic Absorption Method (0.006 % to 1.00 %) 208–217
iron, gray cast iron (including alloy and austenitic), white cast
Chromium by the Peroxydisulfate Oxidation—Titration Method (0.05
iron, malleable cast iron, and ductile (nodular) iron having
% to 30.0 %) 218–226
chemical compositions within the following limits:
Chromium by the Peroxydisulfate-Oxidation Titrimetric Method (0.05
%to30.0%)—Discontinued 1980 144–151
Element Composition Range, %
Cobalt by the Ion-Exchange—Potentiometric Titration Method (2.0 %
to 4.5 %) 53–60
Aluminum 0.003 to 0.50
Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.01 % to
Antimony 0.005 to 0.03
4.50 %) 61–70
Arsenic 0.02 to 0.10
Copper by the Neocuproine Spectrophotometric Method (0.03 % to
Bismuth 0.001 to 0.03
7.5 %) 116–125
Boron 0.001 to 0.10
Copper by the Sulfide Precipitation-Electrodeposition Gravimetric
Cadmium 0.001 to 0.005
Method (0.03 % to 7.5 %) 81–88
Carbon 1.25 to 4.50
Lead by the Ion-Exchange—Atomic Absorption Spectrometry
Cerium 0.005 to 0.05
Method (0.001 % to 0.15 %) 126–135
Chromium 0.01 to 30.00
Magnesium by the Atomic Absorption Spectrometry Method (0.002
Cobalt 0.01 to 4.50
% to 0.10 %) 71–80
Copper 0.03 to 7.50
Manganese by the Periodate Spectrophotometric Method (0.10 % to
Lead 0.001 to 0.15
2.00 %) 9–18
Magnesium 0.002 to 0.10
Manganese by the Peroxydisulfate-Arsenite Titrimetric Method (0.10
Manganese 0.06 to 2.50
% to 3.5 %) 152–159
Molybdenum 0.01 to 5.00
Molybdenum by the Ion Exchange–8-Hydroxyquinoline Gravimetric
Nickel 0.01 to 36.00
Method 257–264
Phosphorus 0.01 to 0.90
Molybdenum by the Thiocyanate Spectrophotometric Method (0.01
Selenium 0.001 to 0.06
% to 1.5 %) 196–207
Silicon 0.10 to 6.0
Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 36.00
Sulfur 0.005 to 0.25
%) 168–175
Tellurium 0.001 to 0.35
Nickel by the Ion Exchange-Atomic Absorption Spectrometry Method
Tin 0.001 to 0.35
(0.005 % to 1.00 %) 176–185
Titanium 0.001 to 0.20
Phosphorus by the Alkalimetric Method (0.02 % to 0.90 %) 160–167
Tungsten 0.001 to 0.20
Phosphorus by the Molybdenum Blue Spectrophotometric Method
Vanadium 0.005 to 0.50
(0.02 % to 0.90 %) 19–30
Zinc 0.005 to 0.20
Silicon by the Gravimetric Method (0.1 % to 6.0 %) 46–52
1.2 The test methods in this standard are contained in the Sulfur by the Gravimetric Method—Discontinued 1988 30–36
Sulfur by the Combustion-Iodate Titration Method (0.005 % to
sections indicated below:
0.25 %)—Discontinued 2012 37–45
Sections Sulfur by the Chromatographic Gravimetric Method—Discontinued
1980 136–143
Carbon, Graphitic, by the Direct Combustion Infrared Absorption Tin by the Solvent Extraction-Atomic Absorption Spectrometry
Method (1 % to 3 %) 108–115 Method (0.002 % to 0.10 %) 186–195
Carbon, Total by the Combustion Gravimetric Method (1.25 % to Tin by the Sulfide Precipitation-Iodometric Titration Method (0.01 %
4.50 %)—Discontinued 2012 97–107 to 0.35 %) 89–96
Titanium by the Diantipyrylmethane Spectrophotometric Method
(0.006 % to 0.35 %) 246–256
Vanadium by the Atomic Absorption Spectrometry Method (0.006 %
These test methods are under the jurisdiction of ASTM Committee E01 on
to 0.15 %) 227–236
Analytical Chemistry for Metals, Ores, and Related Materials and are the direct
responsibility of Subcommittee E01.01 on Iron, Steel, and Ferroalloys.
1.3 Procedures for the determination of carbon and sulfur
Current edition approved July 1, 2018. Published September 2018. Originally
not included in these test methods can be found in Test
approved in 1968. Last previous edition approved in 2013 as E351–13. DOI:
Methods E1019.
10.1520/E0351-18.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E351 − 18
1.4 Some of the composition ranges given in 1.1 are too Nitrogen, and Oxygen in Steel, Iron, Nickel, and Cobalt
broad to be covered by a single method and therefore this Alloys by Various Combustion and Inert Gas Fusion
standard contains multiple methods for some elements. The Techniques
user must select the proper method by matching the informa- E1024Guide for Chemical Analysis of Metals and Metal
tion given in the Scope and Interference sections of each Bearing Ores by Flame Atomic Absorption Spectropho-
method with the composition of the alloy to be analyzed. tometry (Withdrawn 2004)
E1601Practice for Conducting an Interlaboratory Study to
1.5 The values stated in SI units are to be regarded as
Evaluate the Performance of an Analytical Method
standard.
E1806Practice for Sampling Steel and Iron for Determina-
1.6 This standard does not purport to address all of the
tion of Chemical Composition
safety concerns, if any, associated with its use. It is the
2.2 Other Document:
responsibility of the user of this standard to establish appro-
ISO 5725Precision of Test Methods—Determination of
priate safety, health, and environmental practices and deter-
Repeatability and Reproducibility for Inter-Laboratory
mine the applicability of regulatory limitations prior to use.
Tests
Specific hazards statements are given in Section 6 and in
special “Warning” paragraphs throughout these Methods.
3. Terminology
1.7 This international standard was developed in accor-
3.1 Fordefinitionsoftermsusedinthesetestmethods,refer
dance with internationally recognized principles on standard-
to Terminology E135.
ization established in the Decision on Principles for the
Development of International Standards, Guides and Recom-
4. Significance and Use
mendations issued by the World Trade Organization Technical
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
specifications, particularly those under the jurisdiction of
2.1 ASTM Standards:
ASTM CommitteeA04 on Iron Castings. It is assumed that all
D1193Specification for Reagent Water
who use these test methods will be trained analysts capable of
E29Practice for Using Significant Digits in Test Data to
performing common laboratory procedures skillfully and
Determine Conformance with Specifications
safely. It is expected that work will be performed in a properly
E50Practices for Apparatus, Reagents, and Safety Consid-
equippedlaboratoryunderappropriatequalitycontrolpractices
erations for Chemical Analysis of Metals, Ores, and
such as those described in Guide E882.
Related Materials
E60Practice for Analysis of Metals, Ores, and Related
5. Apparatus, Reagents, and Instrumental Practices
Materials by Spectrophotometry
E135Terminology 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.
E173Practice for Conducting Interlaboratory Studies of 5.1.1 In the methods specifying spectrophotometric testing,
Methods for Chemical Analysis of Metals (Withdrawn thecellsutilizedtocontainthereferencematerialsolutionsand
1998) sample solutions in spectrophotometers are referred to as
E350Test 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.Thesemethodsrefertoabsorbancemeasurements.Refer
E352TestMethodsforChemicalAnalysisofToolSteelsand to Practices E60 for details.
Other Similar Medium- and High-Alloy Steels
5.2 Reagents:
E353Test 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, it is intended that
Nickel-Iron Alloys
all reagents conform to the specifications of the Committee on
E354 Test Methods for Chemical Analysis of High-
Analytical Reagents of theAmerican Chemical Society where
Temperature,Electrical,Magnetic,andOtherSimilarIron, 5
such specifications are available. Other grades may be used,
Nickel, and Cobalt Alloys
provided it is first ascertained that the reagent is of sufficiently
E882Guide for Accountability and Quality Control in the
high purity to permit its use without lessening the accuracy of
Chemical Analysis Laboratory
the determination.
E1019Test Methods for Determination of Carbon, Sulfur,
Available fromAmerican National Standards Institute (ANSI), 25 W. 43rd St.,
For referenced ASTM standards, visit the ASTM website, www.astm.org, or 4th Floor, New York, NY 10036, http://www.ansi.org.
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Reagent Chemicals, American Chemical Society Specifications, American
Standards volume information, refer to the standard’s Document Summary page on Chemical Society, Washington, DC. For suggestions on the testing of reagents not
the ASTM website. listed by theAmerican Chemical Society, see the United States Pharmacopeia and
The last approved version of this historical standard is referenced on National Formulary,U.S.PharmacopeialConvention,Inc.(USPC),Rockville,MD.
www.astm.org.
E351 − 18
5.2.2 Purity of Water—Unless otherwise indicated, refer- 13. Interferences
ences to water shall be understood to mean reagent water as
13.1 The elements ordinarily present do not interfere.
conforming to Type I or Type II of Specification D1193. Type
HClO treatment, which is used in the procedure, yields
IIIorIVmaybeusediftheyeffectnomeasurablechangeinthe
solutionswhichcanbehighlycoloredduetothepresenceofCr
blank or sample.
(VI) ions. Although these ions and other colored ions in the
5.3 Spectrophotometric Practice—Spectrophotometric sample solution undergo no further change in color quality
practice prescribed in these test methods shall conform to upon treatment with metaperiodate ion, the following precau-
Practice E60. tions must be observed when filter spectrophotometers are
used: Select a filter with maximum transmittance between 545
6. Hazards
nm and 565 nm. The filter must transmit not more than 5% of
6.1 For precautions to be observed in the use of certain its maximum at a wavelength shorter than 530 nm. The band
reagents and equipment in these methods, refer to Practices
width of the filter should be less than 30 nm when measured at
E50. 50% of its maximum transmittance. Similar restrictions apply
with respect to the wavelength region employed when other
7. Sampling
“wide-band” instruments are used.
7.1 For procedures to sample the material, refer to Practice
13.2 The spectral transmittance curve of permanganate ions
E1806.
exhibits two useful minima, one at approximately 526 nm, and
the other at 545 nm. The latter is recommended when a
8. Interlaboratory Studies and Rounding Calculated
“narrow-band” spectrophotometer is used.
Values
8.1 These test methods have been evaluated as directed in 14. Reagents
Practice E173 (withdrawn 1997) or ISO 5725. Practice E173
14.1 Manganese, Standard Solution (1 mL=0.032 mg
has been replaced by Practice E1601. The Reproducibility R2
Mn)—Transfer the equivalent of 0.4000 g of assayed, high-
of E173 corresponds to the Reproducibility Index R of E1601.
purity manganese (purity: 99.99% minimum), to a 500-mL
TheRepeatabilityR1ofE173correspondstotheRepeatability
volumetric flask and dissolve in 20 mL of HNO by heating.
Index r of E1601.
Cool, dilute to volume, and mix. Using a pipet, transfer 20 mL
8.2 Rounding of test results obtained using these test meth-
to a 500-mL volumetric flask, dilute to volume, and mix.
ods shall be performed as directed in ASTM E29, Rounding
14.2 Nitric-Phosphoric Acid Mixture—Cautiously, while
Method, unless an alternative rounding method is specified by
stirring,add100mLofHNO and400mLofH PO to400mL
3 3 4
the customer or applicable material specification.
of water. Cool, dilute to 1 L, and mix. Prepare fresh as needed.
14.3 Potassium Metaperiodate Solution(7.5g/L)—Dissolve
MANGANESE BY THE METAPERIODATE
7.5 g of potassium metaperiodate (KIO ) in 200 mL of hot
SPECTROPHOTOMETRIC METHOD
HNO (1+1), add 400 mL of H PO , cool, dilute to 1 L, and
3 3 4
mix.
9. Scope
14.4 Water, Pretreated with Metaperiodate—Add 20 mL of
9.1 Thistestmethodcoversthedeterminationofmanganese
KIO solution to 1 Lof water, mix, heat at not less than 90 °C
from 0.10 % to 2.00 %.
for 20 min to 30 min, and cool. Use this water to dilute
solutions to volume that have been treated with KIO solution
10. Summary of Method
to oxidize manganese, and thus avoid reduction of permangan-
10.1 Manganous ions are oxidized to permanganate ions by
ate ions by any reducing agents in the untreated water.
reaction with metaperiodate ions. Solutions of the samples are
(Caution—Avoid the use of this water for other purposes.)
fumed with HClO so that the effect of metaperiodate ion is
limited to the oxidation of manganese. Spectrophotometric
15. Preparation of Calibration Curve
absorbance measurement is made at 545 nm.
15.1 Calibration Solutions—Usingpipets,transfer5mL,10
mL,15mL,20mL,and25mLofmanganesestandardsolution
11. Concentration Range
(1 mL=0.032 mg Mn) to 50-mLborosilicate glass volumetric
11.1 The recommended concentration range is 0.15 mg to
flasks, and, if necessary, dilute to approximately 25 mL.
0.8 mg of manganese per 50 mLof solution, using a 1-cm cell
Proceed as directed in 15.3.
(Note 1) and a spectrophotometer with a band width of 10 nm
15.2 Reference Solution—Transfer approximately 25 mL of
or less.
water to a 50-mL borosilicate glass volumetric flask. Proceed
NOTE 1—This method has been written for cells having a 1-cm light
as directed in 15.3.
path and a narrow-band instrument. The concentration range depends
upon band width and spectral region used as well as cell optical path
15.3 Color Development—Add 10 mL of KIO solution,
length. Cells having other dimensions may be used, provided suitable
and heat the solutions at not less than 90 °C for 20 min to 30
adjustments can be made in the amounts of sample and reagents used.
min(Note2).Cool,dilutetovolumewithpretreatedwater,and
mix.
12. Stability of Color
12.1 The color is stable for at least 24 h. NOTE 2—Immersing the flasks in a boiling water bath is a preferred
E351 − 18
means of heating them for the specified period to ensure complete color
16.2 Reagent Blank Solution—Carry a reagent blank
development.
through the entire procedure using the same amounts of all
reagents with the sample omitted.
15.4 Spectrophotometry:
15.4.1 Multiple-Cell Spectrophotometer—Measure the cell
16.3 Color Development—Proceed as directed in 15.3.
correction using the Reference Solution (15.2) in absorption
16.4 Reference Solutions:
cells with a 1-cm light path and using a light band centered at
16.4.1 Background Color Solution—To one of the sample
545 nm. Using the test cell, take the spectrophotometric
aliquots in a 50-mL volumetric flask, add 100 mL of HNO -
absorbance readings of the calibration solutions versus the
H PO mixture, and heat the solution at not less than 90 °C for
3 4
Reference Solution (15.2).
20minto30min(Note2in15.3).Cool,dilutetovolume(with
15.4.2 Single-Cell Spectrophotometer—Transfer a suitable
untreated water), and mix.
portion of the Reference Solution (15.2) to an absorption cell
16.4.2 Reagent Blank Reference Solution—Transfer the re-
with a 1-cm light path and adjust the spectrophotometer to the
agentblanksolution(16.2)tothesamesizevolumetricflaskas
initial setting, using a light band centered at 545 nm. While
usedforthetestsolutionsandtransferthesamesizealiquotsas
maintaining this adjustment, take the spectrophotometric ab-
used for the test solutions to two 50-mL volumetric flasks.
sorbance readings of the calibration solutions.
Treat one portion as directed in 16.3 and use as reference
15.5 Calibration Curve—Follow the instrument manufac-
solution for test samples. Treat the other as directed in 16.4.1
turer’s instructions for generating the calibration curve. Plot
and use as reference solution for Background Color Solutions.
the net spectrophotometric absorbance readings of the calibra-
16.5 Spectrophotometry—Establishthecellcorrectionswith
tion solutions against the milligrams of manganese per 50 mL
theReagentBlankReferencesolutiontobeusedasareference
of solution.
solution for Background Color solutions. Take the spectropho-
tometric absorbance readings of the Background Color Solu-
16. Procedure
tionsandthetestsolutionsversustherespectiveReagentBlank
16.1 Test Solution:
Reference Solutions as directed in 15.4.
16.1.1 Select and weigh a sample as follows:
17. Calculation
Tolerance in
Maganese, Sample Sample Mass, Dilution,
17.1 Convertthenetspectrophotometricabsorbancereading
% Mass, g mg mL
of the test solution and of the background color solution to
0.01 to 0.5 0.80 0.5 100
milligrams of manganese by means of the calibration curve.
0.45 to 1.0 0.35 0.3 100
Calculate the percentage of manganese as follows:
0.85 to 2.0 0.80 0.5 500
Manganese,% 5 A 2 B / C 310 (1)
~ ! ~ !
Transfer it to a 300-mL Erlenmeyer flask.
16.1.2 TodissolvesamplesthatdonotrequireHF,add8mL
where:
to 10 mL of HCl (1+1), and heat. Add HNO as needed to
A = manganese, mg, found in 50 mL of the final test
hastendissolution,andthenadd3mLto4mLinexcess.When
solution,
dissolution is complete, cool, then add 10 mL of HClO ;
B = apparent manganese, mg, found in 50 mL of the final
evaporate to fumes to oxidize chromium, if present, and to
background color solution, and
expelHCl.Continuefuminguntilsaltsbegintoseparate.Cool,
C = sample mass, g, represented in 50 mL of the final test
add 50 mL of water, and digest if necessary to dissolve the
solution.
salts. Cool and transfer the solution to either a 100-mL or
500-mL volumetric flask as indicated in 16.1.1. Proceed to
18. Precision and Bias
16.1.4.
18.1 Precision—Nine laboratories cooperated in testing this
16.1.3 For samples whose dissolution is hastened by HF,
methodandobtainedthedatasummarizedinTable1.Although
treat them by adding 8 mL to 10 mL of HCl (1+1), and
a sample covered by this method with manganese composition
heating.Add HNO and a few drops of HF as needed to hasten
of approximately 2.0 % was not available, the precision data
dissolution, and then add 3 mL to 4 mL of HNO . When
for this composition should be similar to those obtained for
dissolution is complete, cool, then add 10 mL of HClO ,
material 5.
evaporate to fumes to oxidize chromium, if present, and to
expelHCl.Continuefuminguntilsaltsbegintoseparate.Cool,
add 50 mL of water, digest if necessary to dissolve the salts,
TABLE 1 Statistical Information—Manganese by the
Metaperiodate Spectrophotometric Method
cool, and transfer the solution to either a 100-mL or 500-mL
volumetric flask as indicated in 16.1.1.
Man- Repeat- Repro-
ganese ability ducibil-
16.1.4 Cool the solution to room temperature, dilute to
Test Specimen
Found, (R , ity (R ,
1 2
volume, and mix.Allow insoluble matter to settle, or dry-filter
% E173) E173)
through a coarse paper and discard the first 15 mLto 20 mLof
1. White cast iron (NIST 3a, 0.317 Mn) 0.318 0.006 0.017
the filtrate, before taking aliquots.
2. Cast iron (NIST 4i, 0.793 Mn) 0.793 0.018 0.028
3. Cast iron (B.C.S. 236/2, 1.14 Mn) 1.15 0.03 0.06
16.1.5 Using a pipet, transfer 20 mLaliquots, to two 50-mL
4. White cast iron (NIST 1175, 1.64 Mn) 1.64 0.02 0.08
borosilicate glass volumetric flasks. Treat one portion as
5. Low-alloy steel (NIST 100b, 1.89 Mn) 1.91 0.02 0.04
directed in 16.3. Treat the other portion as directed in 16.4.1.
E351 − 18
18.2 Bias—The accuracy of this test method has been 25.3 Hydrazine Sulfate Solution (1.5 g/L)—Dissolve 1.5 g
deemed satisfactory based upon the data for the certified of hydrazine sulfate ((NH ) ·H SO ) in water, dilute to 1 L,
2 2 2 4
reference materials in Table 1. Users are encouraged to use and mix. Discard any unused solution after 24 h.
these or similar reference materials to verify that the test
25.4 Phosphorus Standard Solution A (1 mL = 1.0 mg
method is performing accurately in their laboratories.
P)—Transfer 2.292 g of anhydrous disodium hydrogen phos-
phate(Na HPO ),previouslydriedtoconstantmassat105°C,
2 4
to a 500-mL volumetric flask; dissolve in about 100 mL of
PHOSPHORUS BY THE MOLYBDENUM BLUE
water, dilute to volume, and mix.
SPECTROPHOTOMETRIC METHOD
25.5 Phosphorus Standard Solution B (1 mL = 0.01 mg
19. Scope
P)—Using a pipet, transfer 10 mL of Solution A (1 mL = 1.0
19.1 This method covers the determination of phosphorus
mg P) to a 1-Lvolumetric flask, add 50 mLof HClO (1 + 5),
from 0.02 % to 0.90 %.
dilute to volume, and mix.
25.6 Phosphorus Standard Solution C (1 mL = 0.10 mg
20. Summary of Method
P)—Using a pipet, transfer 50 mL of Solution A (1 mL = 1.0
20.1 The sample is dissolved in mixed acids and the
mg P) to a 500-mL volumetric flask, add 50 mL of HClO (1
solutionisfumedwithHClO .Ammoniummolybdateisadded
+ 5), dilute to volume, and mix.
to react with the phosphorus to form the heteropoly phospho-
25.7 Sodium Sulfite Solution (100 g/L)—Dissolve 100 g of
molybdate.This species is then reduced with hydrazine sulfate
sodium sulfite (Na SO ) in water, dilute to 1 L, and mix.
2 3
to form the molybdenum blue complex. Spectrophotometric
absorbance measurement is made at 650 nm or 825 nm,
26. Preparation of Calibration Curve for Concentrations
depending upon the concentration.
from 0.005 mg/100 mL to 0.05 mg/100 mL
21. Concentration Range
26.1 Calibration Solutions—Usingpipets,transfer5mL,10
mL, 15 mL, 25 mL, and 50 mL of Phosphorus Standard
21.1 The recommended concentration range is from 0.005
mg to 0.05 mg of phosphorus per 100 mL of solution when Solution B (1 mL = 0.01 mg P) to 100-mL volumetric flasks.
Add20mLofHClO ,dilutetovolume,andmix.Usingapipet,
measuredat825nmandfrom0.05mgto0.3mgofphosphorus
per 100 mL of solution when measured at 650 nm, using a transfer 10 mLof each solution to a 100-mLborosilicate glass
volumetric flask. Proceed as directed in 26.3.
1-cm cell.
NOTE3—Thistestmethodhasbeenwrittenforcellshavinga1-cmlight
26.2 Reagent Blank—Transfer 12 mLof HClO (1+5)toa
path. Cells having other dimensions may be used, provided suitable
100-mL borosilicate glass volumetric flask.
adjustments can be made in the amounts of sample and reagents used.
26.3 Color Development:
22. Stability of Color
26.3.1 Add 15 mLof Na SO solution, boil gently for 30 s,
2 3
22.1 The molybdenum blue complex is stable for at least 2
and add 50 mL of ammonium molybdate-hydrazine sulfate
h.
solution that has been prepared within the hour.
26.3.2 Heat the solutions at not less than 90 °C for 20 min,
23. Interferences
quickly cool, dilute to volume, and mix.
23.1 None of the elements usually present interfere except
NOTE 4—Immersing the flasks in a boiling water bath is the preferred
arsenic, which is removed by volatilization as the bromide.
means of heating them for complete color development.
26.4 Reference Solution—Water.
24. Apparatus
26.5 Spectrophotometry:
24.1 Glassware must be phosphorus- and arsenic-free. Boil
the glassware with HCl and rinse with water before use. It is
26.5.1 Multiple-Cell Spectrophotometer—Measure the re-
recommendedthattheglasswareusedforthisdeterminationbe agent blank (which includes the cell correction) versus the
reservedforthisuseonly.Manydetergentscontainphosphorus
reference solution (26.4) using absorption cells with a 1-cm
and must not be used for cleaning purposes. lightpathandusingalightbandcenteredat825nm.Usingthe
test cell, take the spectrophotometric absorbance readings of
25. Reagents
the calibration solutions versus the reference solution.
26.5.2 Single-Cell Spectrophotometer—Transfer a suitable
25.1 Ammonium Molybdate Solution (20 g/L)—Cautiously,
portion of the reference solution (26.4) to an absorption cell
whilestirringandcooling,add300mLofH SO to500mLof
2 4
with a 1-cm light path and adjust the spectrophotometer to the
water and cool. Add 20 g of ammonium heptamolybdate
initial setting using a light band centered at 825 nm. While
((NH ) Mo O ·4H O), cautiously dilute to 1 L, and mix.
4 6 7 24 2
maintaining this adjustment, take the spectrophotometric ab-
25.2 Ammonium Molybdate-Hydrazine Sulfate Solution—
sorbance readings of the reagent blank solution and of the
Dilute 250 mL of the ammonium molybdate solution to 600
calibration solutions.
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 26.6 Calibration Curve—Follow the instrument manufac-
1h. turer’s instructions for generating the calibration curve. Plot
E351 − 18
the net spectrophotometric absorbance readings of the calibra- tosettleordryfilterthesolution.Usingapipet,transfer10-mL
tionsolutionsagainstthemilligramsofphosphorusper100mL portions to two 100-mL borosilicate glass volumetric flasks;
of solution. treat one as directed in 28.3 and the other as directed in 28.4.2.
28.1.3 Treat samples of white iron as directed in 28.1.3.1
27. Preparation of Calibration Curve for Concentrations
and 28.1.3.2.
from 0.05 mg/100 mL to 0.30 mg/100 mL
28.1.3.1 Crush the material in an iron mortar and weigh
27.1 Calibration Solutions—Usingpipets,transfer5mL,10
only particles passing through a 300-µm (No. 50) sieve.
mL,15mL,20mL,25mL,and30mLofPhosphorusStandard
Transfer the weighed sample to a 250-mL Erlenmeyer flask.
Solution C (1 mL = 0.10 mg P) to 100-mL volumetric flasks.
Add 15 mL of HNO and 5 mL of HBr. Heat until dissolution
Add20mLofHClO ,dilutetovolume,andmix.Usingapipet,
4 is complete.Add 10 mLof HClO , evaporate to copious white
transfer 10 mLof each solution to a 100-mLborosilicate glass
fumes; then, without delay, fume strongly enough to cause the
volumetric flask.
white fumes to clear the neck of the flask, and continue at this
rate for 1 min.
27.2 Reagent Blank—Proceed as directed in 26.2.
28.1.3.2 Coolthesolution,add60mLofHClO (1+5),and
27.3 Color Development—Proceed as directed in 26.3.
swirl to dissolve the salts. Transfer to a 100-mL volumetric
27.4 Reference Solution—Water.
flask, cool, dilute to volume, and mix. Allow insoluble matter
tosettleordryfilterthesolution.Usingapipet,transfer10-mL
27.5 Spectrophotometry:
portions to two 100-mL borosilicate glass volumetric flasks;
27.5.1 Multiple-Cell Spectrophotometer—Measure the re-
treat one as directed in 28.3 and the other as directed in 28.4.2.
agent blank (which includes the cell correction) versus the
reference solution (27.4) using absorption cells with a 1-cm
28.2 Reagent Blank Solution—Carry a reagent blank
light path and a light band centered at 650 nm. Using the test
through the entire procedure using the same amount of all
cell, take the spectrophotometric absorbance readings of the
reagents with the sample omitted.
calibration solutions versus the reference solution.
28.3 Color Development—Proceed with one of the 10-mL
27.5.2 Single-Cell Spectrophotometer—Transfer a suitable
portions obtained in 28.1.2.2 or 28.1.3.2, as directed in 26.3.
portion of the reference solution (27.4) to an absorption cell
with a 1-cm light path and adjust the spectrophotometer to the
28.4 Reference Solutions:
initial setting using a light band (no change) centered at 650
28.4.1 Water—Use this as the reference solution for the
nm. While maintaining this adjustment, take the spectrophoto-
reagent blank solution.
metricabsorbancereadingsofthereagentblanksolutionandof
28.4.2 Background Color Reference Solution—Add 15 mL
the calibration solutions.
of Na SO solution to the second 10-mL portion obtained in
2 3
27.6 Calibration Curve—Follow the instrument manufac-
28.1.2.2 or 28.1.3.2. Boil gently for 30 s, add 50 mLof H SO
2 4
turer’s instructions for generating the calibration curve. Plot
(3 + 37), cool, dilute to volume, and mix. Use this as the
the net spectrophotometric absorbance readings of the calibra-
reference solution for the test solution.
tionsolutionsagainstthemilligramsofphosphorusper100mL
28.5 Spectrophotometry—Take the spectrophotometric ab-
of solution.
sorbance readings of the reagent blank solution and of the test
28. Procedure solution (using the respective reference solutions) as directed
in 26.5 or 27.5 depending upon the estimated composition of
28.1 Test Solution:
phosphorus in the sample.
28.1.1 Select and weigh a sample as follows:
Sample Tolerance in
29. Calculation
Phosphorus, % Mass, g Sample Mass, mg
29.1 Convertthenetspectrophotometricabsorbancereading
0.020 to 0.30 1.0 0.5
0.30 to 0.60 0.5 0.3 of the test solution and of the reagent blank solution to
0.60 to 0.90 0.25 0.1
milligrams of phosphorus by means of the appropriate calibra-
Transfer it to a 250-mL Erlenmeyer flask.
tion curve. Calculate the percent of phosphorus as follows:
28.1.2 If the sample is other than white iron, proceed as
Phosphorus,% 5 ~A 2 B!⁄~C 3 10! (2)
directed in 28.1.2.1 and 28.1.2.2.
28.1.2.1 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
TABLE 2 Statistical Information—Phosphorus—Molybdenum
and evaporate to fumes. Remove the flask immediately to
Blue—Spectrophotometric Method
avoid undue loss of HClO , cool, and add 20 mL of HBr (1 +
Phos- Repeat- Repro-
4). Evaporate the solution to copious white fumes and then,
phorus ability ducibil-
Test Specimen
without delay, fume strongly enough to cause the white fumes Found, (R , ity (R ,
1 2
% E173) E173)
tocleartheneckoftheflask,andcontinueatthisratefor1min.
1. Cast iron 15Ni-2Cr-5Cu (NIST 115, 0.114 P) 0.107 0.013 0.014
28.1.2.2 Coolthesolution,add60mLofHClO (1+5),and
2. Cast iron (NIST 5k, 0.263 P) 0.257 0.016 0.012
swirl to dissolve the salts. Transfer to a 100-mL volumetric
3. Cast iron (NIST 7g, 0.794 P) 0.779 0.020 0.053
flask, cool, dilute to volume, and mix. Allow insoluble matter
E351 − 18
where: % silicon for samples containing more than 0.10 % by
determining duplicate values for silicon as directed in 49.2.2 –
A = phosphorus found in 100 mL of the final test solution,
49.2.6.
mg,
49.2.2 Transfer 15 mL of HClO (Note 5) to each of two
B = phosphorus found in 100 mL of the final reagent blank
400-mL beakers. To one of the beakers transfer an additional
solution, mg, and
C = sample represented in 100 mL of the final test solution, 50 mL of HClO . Using a pipet, transfer 20 mL of Na SiO
4 2 3
solution(1mL=1.00mgSi)toeachofthebeakers.Evaporate
g.
the solutions to fumes and heat for 15 min to 20 min at such a
30. Precision and Bias
rate that HClO refluxes on the sides of the beakers. Cool
sufficiently, and add 100 mL of water (40 °C to 50 °C).
30.1 Precision—Nine laboratories cooperated in testing this
method and obtained the data summarized in Table 2.
NOTE5—The15-mLadditionofHClO canbefromthesamelotasthe
onetobetested.Oncealothasbeenestablishedashavinglessthan0.0002
30.2 Bias—The accuracy of this test method exhibits a
% silicon, it should preferably be used for the 15-mL addition in all
slight negative bias based upon the data for the certified
subsequent tests of other lots of acid.
reference materials in Table 2. Users are encouraged to use
these or similar reference materials to verify that the test 49.2.3 Addpaperpulpandfilterimmediately,usinglow-ash
method is performing accurately in their laboratories. 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
SULFUR BY THE GRAVIMETRIC METHOD
with 3-mLto 5-mLportions of hot HCl (1 + 19) and hot water,
foratotalof6times.FinallywashthepaperstwicewithH SO
2 4
This test method, which consisted of Sections 30 through 36,
(1 + 49). Transfer the papers to platinum crucibles.
was discontinued in 1988.
49.2.4 Dry the papers and heat at 600 °C until the carbon is
SULFUR BY THE COMBUSTION-IODATE
removed.Finallyigniteat1100°Cto1150°Ctoconstantmass
TITRATION METHOD
(at least 30 min). Cool in a desiccator and weigh.
49.2.5 Add enough H SO (1 + 1) to moisten the SiO , and
2 4 2
This test method, which consisted of Sections 37 through 45,
add 3 mL to 5 mL of HF. Evaporate to dryness and then heat
was discontinued in 2012.
at a gradually increasing rate until H SO is removed. Ignite
2 4
for 15 min at 1100 °C to 1150 °C, cool in a desiccator, and
SILICON BY THE GRAVIMETRIC METHOD
weigh.
49.2.6 Calculate the percent of silicon as follows:
46. Scope
Silicon,% 5 A 2 B 2 C 2 D 30.4674⁄E 3100 (3)
@~ ! ~ !#
46.1 This method covers the determination of silicon from
0.1 % to 6.1 %. where:
A = initialmassofcrucibleplusimpureSiO when65mLof
47. Summary of Test Method
HClO was taken, g,
47.1 After dissolution of the sample, silicic acid is dehy-
B = final mass of crucible plus impurities when 65 mL of
drated by fuming with H SO or HClO . The solution is
HClO was taken, g,
2 4 4
filtered,andtheimpuresilicaisignitedandweighed.Thesilica C = initialmassofcrucibleplusimpureSiO when15mLof
isthenvolatilizedwithHF.Theresidueisignitedandweighed; HClO was taken, g,
D = final mass of crucible plus impurities when 15 mL of
the loss in mass represents silica.
HClO was taken, g, and
48. Interferences
E = nominal mass (80 g) of 50 mL of HClO .
48.1 Theelementsordinarilypresentdonotinterfereiftheir
49.3 Sodium Silicate Solution—Transfer 11.0 g of sodium
compositions are under the maximum limits shown in 1.1.
silicate (Na SiO ·9H O) to a 400-mL beaker. Add 150 mL of
2 3 2
water and dissolve the salt. Filter through a medium paper,
49. Reagents
collecting the filtrate in a 1-L volumetric flask, dilute to
49.1 The analyst should ensure by analyzing blanks and
volume, and mix. Store in a polyethylene bottle. Use this
other checks that possible silicon contamination of reagents
solution to determine the suitability of the HClO .
will not significantly bias the results.
49.4 Tartaric Acid Solution (20.6 g/L)—Dissolve 20.6 g of
49.2 Perchloric Acid (HClO ):
tartaric acid (C H O ) in water, dilute to 1 L, and filter.
4 6 6
49.2.1 Select a lot of HClO that contains not more than
0.0002 % silicon for the analysis of samples containing silicon 49.5 Water—Use freshly prepared Type II water known to
in the range from 0.02 % to 0.10 % and not more than 0.0004 be free of silicon. Water distilled from glass, demineralized in
E351 − 18
TABLE 3 Statistical Information—Silicon—Gravimetric Method
columns containing silicon compounds, or stored for extended
periods in glass, or combination thereof, has been known to Repeat- Repro-
Silicon
ability ducibil-
absorb silicon.
Test Specimen Found,
(R , ity (R ,
1 2
%
E173) E173)
50. Procedure
HClO Dehydration
50.1 Select and weigh a sample as follows:
1. Cast iron 1.2Ni-0.3Cr-0.8 Mo (NIST 1.36 0.02 0.02
107b, 1.35 Si)
Tolerance Dehydrating Acid, mL
2. Cast iron (NIST 4i, 1.45 Si) 1.45 0.04 0.05
Sample in Sample H SO
2 4
3. Cast iron 1.07Ni-0.32Cr (NIST 82a, 2.08 0.04 0.05
Silicon, % Mass, g Mass, mg (1+4) HClO
2.07 Si)
4. Cast iron (NIST 5k, 2.08 Si) 2.08 0.03 0.05
0.10 to 1.00 4.0 4 150 60
5. Cast iron, high (0.79) phosphorus 2.40 0.04 0.07
1.00 to 2.00 3.0 3 100 50
(NIST 7g, 2.41 Si)
2.00 to 4.00 2.0 2 100 40
6. White cast iron (NIST 1176, 3.19 Si) 3.20 0.03 0.10
4.00 to 6.00 1.0 1 100 40
H SO Dehydration
2 4
Transfer it to a 400-mL beaker or a 300-mL porcelain
1. Cast iron 1.2Ni-0.3Cr-0.8Mo (NIST 1.36 0.02 0.03
107b, 1.35 Si)
casserole.
2. Cast iron (NIST 4i, 1.45 Si) 1.45 0.04 0.06
3. Cast iron 1.07Ni-0.32Cr (NIST 82a, 2.08 0.04 0.04
50.2 If the sample type is other than white iron, proceed as
2.07 Si)
directed in 50.3; treat samples of white iron as directed in
4. Cast iron (NIST 5k, 2.08 Si) 2.08 0.04 0.05
50.2.1.
5. Cast iron, high (0.79) phosphorus 2.41 0.03 0.05
(NIST 7g, 2.41 Si)
50.2.1 Crush the material in an iron mortar and use only
particles passing through a 150-µm (No. 100) sieve. Add 30
mLofHNO and10mLofHBr.Whenthedissolutionreaction
becomes passive, decant the bulk of the solution to a 400-mL
beaker and crush the remaining insoluble matter in the original
dehydrating acid used. Filter immediately, using a low-ash,
beaker with a glass rod. Add 20 mL of HNO and 10 mL of
3 9-cm-100-porosity filter paper, and wash as directed in 50.3.
HBr, and heat gently until dissolution is complete. Combine
50.5 Transfer the paper and precipitate to the reserved
the two portions of the solution and add the amount of H SO
2 4
platinum crucible. Dry the papers and then heat the crucible at
or HClO specified in 50.1.
600 °C until the carbon is removed. Finally ignite at 1100 °C
50.2.2 H SO Dehydration:
2 4
to 1150 °C to constant mass (at least 30 min). Cool in a
50.2.2.1 Evaporate until salts begin to separate; at this point
desiccator and weigh.
evaporate the solution rapidly to the first appearance of fumes
50.6 Add enough H SO (1 + 1) to moisten the impure
andfumestronglyfor2minto3min.Coolsufficiently,andadd
2 4
SiO , and add 3 mL to 5 mL of HF. Evaporate to dryness and
100mLofwater(40°Cto50°C).Stirtodissolvethesaltsand
thenheatatagraduallyincreasingrateuntilH SO isremoved.
heat, if necessary, but do not boil. Proceed immediately as
2 4
Ignite at 1100 °C to 1150 °C for 15 min, cool in a desiccator,
directed in 50.4.
and weigh.
50.2.3 HClO Dehydration:
50.2.3.1 Evaporate the solution to fumes and heat for 15
51. Calculation
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
51.1 Calculate the percent of silicon as follows:
water (40 °C to 50 °C). Stir to dissolve the salts and heat to
Silicon,% 5 @~~A 2 B! 3 0.4674!⁄C# 3100 (4)
boiling. If the sample solution contains more than 100 mg of
chromium,add,whilestirring,1mLoftartaricacidsolutionfor where:
each 25 mg of chromium.
A = initial mass of crucible and impure SiO,g,
B = final mass of crucible and residue, g, and
50.3 Add paper pulp and filter immediately, on a low-ash
C = sample used, g.
11-cm medium-porosity filter paper. Collect the filtrate in a
600-mLbeaker.Transfer the precipitate to the paper, and scrub
52. Precision and Bias
the container thoroughly with a rubber-tipped rod. Wash the
paperandprecipitatealternatelywith3-mLto5-mLportionsof 52.1 Precision—Eleven laboratories cooperated in testing
hot HCl (1 + 19) and hot water until iron salts are removed but this method and obtained the data summarized in Table 3.
Although samples covered by this method with silicon com-
for not more than a total of ten washings. If the HClO
dehydration method was followed, wash the paper twice more positions near the extreme limits of the scope were not
available for testing, the precision data obtained for low-alloy
with H SO (1 + 49), but do not collect these washings in the
2 4
filtrate; discard the washings. Transfer the paper to a platinum steels by Test Methods E350 should apply at the lower limit.
crucible and reserve.
52.2 Bias—The accuracy of this test method has been
50.4 Add 15 mLof HNO to the filtrate, stir, and evaporate deemed satisfactory based upon the data for the certified
as directed in either 50.2.2 or 50.2.3, depending upon the reference materials in Table 3. Users are encouraged to use
E351 − 18
these or similar reference materials to verify that the test having a nominal crosslinkage of 8 %, and 0.075-mm to
method is performing accurately in their laboratories. 0.037-mm (200-nominal to 400-nominal mesh) size. To re-
move those beads greater than about 180-µm in diameter as
well as the excessively fine beads, treat the resin as follows:
COBALT BY THE ION-EXCHANGE-
Transferasupplyoftheresintoabeaker,coverwithwater,and
POTENTIOMETRIC TITRATION METHOD
allow sufficient time (at least 30 min) for the beads to undergo
maximum swelling. Place a 180-µm (No. 80) screen, 150 mm
53. Scope
indiameterovera2-Lbeaker.Prepareathinslurryoftheresin
53.1 This test method covers the determination of cobalt
and pour it onto the screen. Wash the fine beads through the
from 2.0 % to 4.5 %.
screen, using a small stream of water. Discard the beads
retained on the screen, periodically, if necessary, to avoid
54. Summary of Method
unduecloggingoftheopenings.Whenthebulkofthecollected
54.1 Cobalt is separated from interfering elements by selec-
resin has settled, decant the water and transfer approximately
tive elution from an anion-exchange column using HCl. The
100 mLof resin to a 400-mLbeaker.Add 200 mLof HCl (1 +
cobalt is oxidized to the trivalent state with ferricyanide, and
19),stirvigorously,allowtheresintosettlefor4minto6min,
the excess ferricyanide is titrated potentiometrically with
decant 150 mL to 175 mL of the suspension, and discard.
cobalt solution.
RepeatthetreatmentwithHCl(1+19)twicemore,andreserve
55. Interferences
the coarser resin for the column preparation.
55.1 The elements normally present do not interfere if their 57.3.2 Prepare the column as follows: Place a 10-mm to
compositions are under the maximum limits shown in 1.1. 20-mmlayerofglasswoolorpolyvinylchlorideplasticfiberin
the bottom of the column, and add a sufficient amount of the
56. Apparatus
prepared resin to fill the column to a height of approximately
56.1 Ion-Exchange Column,approximately25mmindiam- 140 mm. Place a 20-mm layer of glass wool or polyvinyl
eter and 300 mm in length, tapered at one end, and provided
chloride plastic fiber at the top of the resin bed to protect it
with a stopcock to control the flow rate, and a second, lower
from being carried into suspension when the solutions are
stopcocktostoptheflow.AJonesReductor,maybeadaptedto
added. While passing a minimum of 35 mL of HCl (7 + 5)
thismethod.Areservoirfortheeluantsmaybeaddedatthetop
through the column, with the hydrostatic head 100 mm above
of the column.
the top of the resin bed, adjust the flow rate to not more than
3.0mLpermin.Drainto10mmto20mmabovethetopofthe
56.2 pH meter, with a platinum and a saturated calomel
resin bed and then close the lower stopcock.
electrode.
NOTE 6—The maximum limits of 0.125 g of cobalt and 0.500 g in the
57. Reagents
sample solution take into account the exchange capacity of the resin, the
57.1 Ammonium Citrate Solution (200 g/l)—Dissolve 200 g
physical dimensions of the column, and the volume of eluants.
of di–ammonium hydrogen citrate in water and dilute to 1 L.
57.4 Potassium Ferricyanide, Standard Solution (1
57.2 Cobalt, Standard Solution (1mL = 1.5 mg of Co).
mL=3.0 mg of Co):
57.2.1 Preparation—Dry a weighing bottle in an oven at
57.4.1 Dissolve 16.68 g of potassium ferricyanide
130 °C for 1 h, cool in a desiccator, and weigh.Transfer 3.945
6 (K Fe(CN) ) in water and dilute to 1 L. Store the solution in a
3 6
g of cobalt sulfate (CoSO ) that has been heated at 550 °C for
dark-colored bottle. Standardize the solution each day before
1 h to the weighing bottle. Dry the bottle and contents at 130
use as follows: Transfer from a 50-mLburet approximately 20
°C for 1 h, cool in desiccator, stopper the bottle, and weigh.
mL of K Fe(CN) solution to a 400-mL beaker. Record the
3 6
The difference in mass is the amount of CoSO taken.Transfer
buret reading to the nearest 0.01 mL.Add 25 mL of water, 10
the weighed CoSO to a 400-mL beaker, rinse the weighing
mLofammoniumcitratesolution,and25mLofNH OH.Cool
bottle with water, and transfer the rinsings to the beaker. Add 4
to 5 °C to 10 °C, and maintain this temperature during the
150 mLof water and 20 mLof HNO , and heat to dissolve the
titration. Transfer the beaker to the potentiometric titration
salts.Cool,transfertoa1-Lvolumetricflask,dilutetovolume,
apparatus.Whilestirring,titratetheK Fe(CN) withthecoba
...


This document is not an ASTM standard and is intended only to provide the user of an ASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation: E351 − 13 E351 − 18
Standard Test Methods for
Chemical Analysis of Cast Iron—All Types
This standard is issued under the fixed designation E351; 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.
This standard has been approved for use by agencies of the U.S. Department of Defense.
1. Scope
1.1 These test methods cover the chemical analysis of pig iron, gray cast iron (including alloy and austenitic), white cast iron,
malleable cast iron, and ductile (nodular) iron having chemical compositions within the following limits:
Element Composition Range, %
Aluminum 0.003 to 0.50
Antimony 0.005 to 0.03
Arsenic 0.02 to 0.10
Bismuth 0.001 to 0.03
Boron 0.001 to 0.10
Cadmium 0.001 to 0.005
Carbon 1.25 to 4.50
Cerium 0.005 to 0.05
Chromium 0.01 to 30.00
Cobalt 0.01 to 4.50
Copper 0.03 to 7.50
Lead 0.001 to 0.15
Magnesium 0.002 to 0.10
Manganese 0.06 to 2.50
Molybdenum 0.01 to 5.00
Nickel 0.01 to 36.00
Phosphorus 0.01 to 0.90
Selenium 0.001 to 0.06
Silicon 0.10 to 6.0
Sulfur 0.005 to 0.25
Tellurium 0.001 to 0.35
Tin 0.001 to 0.35
Titanium 0.001 to 0.20
Tungsten 0.001 to 0.20
Vanadium 0.005 to 0.50
Zinc 0.005 to 0.20
1.2 The test methods in this standard are contained in the sections indicated below:
Sections
Carbon, Graphitic, by the Direct Combustion Infrared Absorption
Method (1 % to 3 %) 108
Carbon, Graphitic, by the Direct Combustion Infrared Absorption
Method (1 % to 3 %) 108–115
Carbon, Total by the Combustion Gravimetric Method (1.25 % to
4.50 %)—Discontinued 97
Carbon, Total by the Combustion Gravimetric Method (1.25 % to
4.50 %)—Discontinued 2012 97–107
Cerium and Lanthanum by the Direct Current Plasma Atomic
Emission Spectrometry Method (Ce: 0.003 % to 0.5 %; La: 0.001
% to 0.30 %) 237
Cerium and Lanthanum by the Direct Current Plasma Atomic
Emission Spectrometry Method (Ce: 0.003 % to 0.5 %; La: 0.001
% to 0.30 %) 237–245
Chromium by the Atomic Absorption Method (0.006 % to 1.00 %) 208
These test methods are under the jurisdiction of 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 Feb. 1, 2013July 1, 2018. Published May 2013September 2018. Originally approved in 1968. Last previous edition approved in 20062013 as
E351 – 93E351 – 13. (Reapproved 2006). DOI: 10.1520/E0351-13.10.1520/E0351-18.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E351 − 18
Chromium by the Atomic Absorption Method (0.006 % to 1.00 %) 208–217
Chromium by the Peroxydisulfate Oxidation—Titration Method
(0.006 % to 1.00 %) 218
Chromium by the Peroxydisulfate Oxidation—Titration Method (0.05
% to 30.0 %) 218–226
Chromium by the Peroxydisulfate-Oxidation Titrimetric Method (0.05
% to 30.0 %)—Discontinued 1980 144–151
Cobalt by the Ion-Exchange—Potentiometric Titration Method (2.0 %
to 4.5 %) 53
Cobalt by the Ion-Exchange—Potentiometric Titration Method (2.0 %
to 4.5 %) 53–60
Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.01 % to
4.50 %) 61
Cobalt by the Nitroso-R-Salt Spectrophotometric Method (0.01 % to
4.50 %) 61–70
Copper by the Neocuproine Spectrophotometric Method (0.03 % to
7.5 %) 116
Copper by the Neocuproine Spectrophotometric Method (0.03 % to
7.5 %) 116–125
Copper by the Sulfide Precipitation-Electrodeposition Gravimetric
Method (0.03 % to 7.5 %) 81
Copper by the Sulfide Precipitation-Electrodeposition Gravimetric
Method (0.03 % to 7.5 %) 81–88
Lead by the Ion-Exchange—Atomic Absorption Method (0.001 % to
0.15 %) 126
Lead by the Ion-Exchange—Atomic Absorption Spectrometry
Method (0.001 % to 0.15 %) 126–135
Magnesium by the Atomic Absorption Method (0.002 % to 0.10 %) 71
Magnesium by the Atomic Absorption Spectrometry Method (0.002
% to 0.10 %) 71–80
Manganese by the Periodate Spectrophotometric Method (0.10 % to
2.00 %) 8
Manganese by the Periodate Spectrophotometric Method (0.10 % to
2.00 %) 9–18
Manganese by the Peroxydisulfate-Arsenite Titrimetric Method (0.10
% to 3.5 %) 152
Manganese by the Peroxydisulfate-Arsenite Titrimetric Method (0.10
% to 3.5 %) 152–159
Molybdenum by the Ion Exchange–8-Hydroxyquinoline Gravimetric
Method 257
Molybdenum by the Ion Exchange–8-Hydroxyquinoline Gravimetric
Method 257–264
Molybdenum by the Spectrophotometric Method (0.01 % to 1.5 %) 196
Molybdenum by the Thiocyanate Spectrophotometric Method (0.01
% to 1.5 %) 196–207
Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 36.00
%) 168
Nickel by the Dimethylglyoxime Gravimetric Method (0.1 % to 36.00
%) 168–175
Nickel by the Ion Exchange-Atomic Absorption Method (0.005 % to
1.00 %) 176
Nickel by the Ion Exchange-Atomic Absorption Spectrometry Method
(0.005 % to 1.00 %) 176–185
Phosphorus by the Alkalimetric Method (0.02 % to 0.90 %) 160
Phosphorus by the Alkalimetric Method (0.02 % to 0.90 %) 160–167
Phosphorus by the Molybdenum Blue Spectrophotometric Method
(0.02 % to 0.90 %) 18
Phosphorus by the Molybdenum Blue Spectrophotometric Method
(0.02 % to 0.90 %) 19–30
Silicon by the Gravimetric Method (0.1 % to 6.0 %) 46
Silicon by the Gravimetric Method (0.1 % to 6.0 %) 46–52
Sulfur by the Gravimetric Method—Discontinued 30
Sulfur by the Gravimetric Method—Discontinued 1988 30–36
Sulfur by the Combustion-Iodate Titration Method (0.005 % to
0.25 %)—Discontinued 37
Sulfur by the Combustion-Iodate Titration Method (0.005 % to
0.25 %)—Discontinued 2012 37–45
Sulfur by the Chromatographic Gravimetric Method—Discontinued
1980 136–143
Tin by the Solvent Extraction-Atomic Absorption Method (0.002 % to
0.10 %) 186
Tin by the Solvent Extraction-Atomic Absorption Spectrometry
Method (0.002 % to 0.10 %) 186–195
Tin by the Sulfide-Iodometric Titration Method (0.01 % to 0.35 %) 89
Tin by the Sulfide Precipitation-Iodometric Titration Method (0.01 %
to 0.35 %) 89–96
Titanium, Total, by the Diantipyrylmethane Spectrophotometric
Method (0.006 % to 0.35 %) 246
E351 − 18
Titanium by the Diantipyrylmethane Spectrophotometric Method
(0.006 % to 0.35 %) 246–256
Vanadium by the Atomic Absorption Method (0.006 % to 0.15 %) 227
Vanadium by the Atomic Absorption Spectrometry Method (0.006 %
to 0.15 %) 227–236
1.3 Procedures for the determination of carbon and sulfur not included in these test methods 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 method and therefore this standard
contains multiple methods for some elements. The user must select the proper method by matching the information given in the
Scope and Interference sections of each 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 safety, health, and healthenvironmental 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 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 1998)
E350 Test Methods for Chemical Analysis of Carbon Steel, Low-Alloy Steel, Silicon Electrical Steel, Ingot Iron, and Wrought
Iron
E352 Test Methods for Chemical Analysis of Tool Steels and Other Similar Medium- and High-Alloy Steels
E353 Test Methods for Chemical Analysis of Stainless, Heat-Resisting, Maraging, and Other Similar Chromium-Nickel-Iron
Alloys
E380E354 Practice for Use of the International System of Units (SI) (the Modernized Metric System)Test Methods for Chemical
Analysis of High-Temperature, Electrical, Magnetic, and Other Similar Iron, Nickel, and Cobalt Alloys (Withdrawn 1997)
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 A04 on
Iron Castings. 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.
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.
Available from American National Standards Institute (ANSI), 25 W. 43rd St., 4th Floor, New York, NY 10036, http://www.ansi.org.
E351 − 18
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, it is intended that all
reagents conform to the specifications of the Committee on Analytical Reagents of the American Chemical Society where such
specifications are available. Other grades may be used, provided it is first ascertained that the reagent is of sufficiently high purity
to permit its use without lessening the accuracy of the determination.
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.
7. Sampling
7.1 For procedures for samplingto sample the material, reference shall be made refer to Practice E1806.
8. Interlaboratory Studies and Rounding Calculated Values
8.1 These test methods have been evaluated in accordance withas directed in 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 E1601E1601. The Repeatability R1 of E173 corresponds to the Repeatability Index r of E1601E1601.
8.2 Calculated values shall be rounded to the desired number of places in accordanceRounding of test results obtained using
these test methods shall be performed as directed in ASTM E29with the Rounding Method of Practice, Rounding Method, unless
an alternative E29. rounding method is specified by the customer or applicable material specification.
MANGANESE BY THE METAPERIODATE SPECTROPHOTOMETRIC METHOD
9. Scope
9.1 This test method covers the determination of manganese in compositions from 0.10 % to 2.00 %.
9. Scope
9.1 This test method covers the determination of manganese from 0.10 % to 2.00 %.
10. Summary of Method
10.1 Manganous ions are oxidized to permanganate ions by reaction with metaperiodate ions. Solutions of the samples are
fumed with HClO so that the effect of metaperiodate ion is limited to the oxidation of manganese. Spectrophotometric absorbance
measurement is made at approximately 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.
Reagent Chemicals, American Chemical Society Specifications, American Chemical Society, Washington, DC. 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.
E351 − 18
13. Interferences
13.1 The elements ordinarily present do not interfere. 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“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“narrow-band” spectrophotometer is used.
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
3 3 4
water. 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. (WarningCaution—
Avoid the use of this water for other purposes.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 approximately 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 approximately 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 Solution:
16.1.1 Select and weigh a sample in accordance with the following:as follows:
Tolerance in
Maganese, Sample Sample Weight, Dilution,
% Weight, g mg mL
Tolerance in
Maganese, Sample Sample Mass, Dilution,
% Mass, g mg mL
0.01 to 0.5 0.80 0.5 100
0.45 to 1.0 0.35 0.3 100
0.85 to 2.0 0.80 0.5 500
E351 − 18
Transfer it to a 300-mL Erlenmeyer flask.
16.1.2 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 16.1.1. Proceed to 16.1.4.
16.1.3 For samples whose dissolution is hastened by HF, treat them by adding 8 mL to 10 mL of HCl (1 + 1), and heating. 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,
3 3
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 16.1.1.
16.1.4 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.
16.1.5 Using a pipet, transfer 20 mL aliquots, 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 100 mL of HNO -H PO
3 3 4
mixture, and heat the solution at not less than 90 °C for 20 min to 30 min (Note 2 in 15.3). 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.
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 310! (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 weight, g, represented in 50 mL of the final test solution.
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. Although a
sample covered by this method with manganese composition of approximately 2.0 % was not available, the precision data for this
composition should be similar to those obtained for material 5.
TABLE 1 Statistical Information—Manganese by the
Metaperiodate Spectrophotometric Method
Man- Repeat- Repro-
ganese ability ducibil-
Test Specimen
Found, (R , ity (R ,
1 2
% E173) E173)
1. White cast iron (NIST 3a, 0.317 Mn) 0.318 0.006 0.017
2. Cast iron (NIST 4i, 0.793 Mn) 0.793 0.018 0.028
3. Cast iron (B.C.S. 236/2, 1.14 Mn) 1.15 0.03 0.06
4. White cast iron (NIST 1175, 1.64 Mn) 1.64 0.02 0.08
5. Low-alloy steel (NIST 100b, 1.89 Mn) 1.91 0.02 0.04
E351 − 18
18.2 Bias—No information on the accuracy of this method is known. The accuracy of this method may be judged by comparing
accepted reference values with the corresponding arithmetic average obtained by interlaboratory testing.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 method covers the determination of phosphorus in compositions from 0.02 % to 0.90 %.
19. Scope
19.1 This method covers the determination of phosphorus from 0.02 % to 0.90 %.
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.
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.
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 weightmass at 105 °C, to a 500-mL volumetric flask; dissolve in about 100 mL of water,
2 4
dilute 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 in accordance withas directed in 26.3.
E351 − 18
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.
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 approximately 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 approximately 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. Preparation of Calibration Curve for Concentrations from 0.05 mg/100 mL to 0.30 mg/100 mL
27.1 Calibration Solutions—Using pipets, transfer 5 mL, 10 mL, 15 mL, 20 mL, 25 mL, and 30 mL of Phosphorus Standard
Solution C (1 mL = 0.10 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.
27.2 Reagent Blank—Proceed in accordance withas directed in 26.2.
27.3 Color Development—Proceed in accordance withas directed in 26.3.
27.4 Reference Solution—Water.
27.5 Spectrophotometry:
27.5.1 Multiple-Cell Spectrophotometer—Measure the reagent blank (which includes the cell correction) versus the reference
solution (27.4) using absorption cells with a 1-cm light path and a light band centered at approximately 650 nm. Using the test
cell, take the spectrophotometric absorbance readings of the calibration solutions versus the reference solution.
27.5.2 Single-Cell Spectrophotometer—Transfer a suitable portion of the reference solution (27.4) to an absorption cell with a
1-cm light path and adjust the spectrophotometer to the initial setting using a light band (no change) centered at approximately
650 nm. While maintaining this adjustment, take the spectrophotometric absorbance readings of the reagent blank solution and of
the calibration solutions.
27.6 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.
28. Procedure
28.1 Test Solution:
28.1.1 Select and weigh a sample in accordance with the following:as follows:
Sample Tolerance in
Phosphorus, % Weight, g Sample Weight, mg
Sample Tolerance in
Phosphorus, % Mass, g Sample Mass, mg
0.020 to 0.30 1.0 0.5
0.30 to 0.60 0.5 0.3
0.60 to 0.90 0.25 0.1
Transfer it to a 250-mL Erlenmeyer flask.
28.1.2 If the sample is other than white iron, proceed as directed in 28.1.2.1 and 28.1.2.2.
28.1.2.1 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.
28.1.2.2 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 in accordance withas directed in 28.3 and the other in accordance
withas directed in 28.4.2.
E351 − 18
28.1.3 Treat samples of white iron as directed in 28.1.3.1 and 28.1.3.2.
28.1.3.1 Crush the material in an iron mortar and weigh only particles passing through a No. 50 (300-μm)300-μm (No. 50) sieve.
Transfer the weighed sample to a 250-mL Erlenmeyer flask. Add 15 mL of HNO and 5 mL of HBr. Heat until dissolution is
complete. Add 10 mL of HClO , evaporate to copious white fumes; 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.
28.1.3.2 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 in accordance withas directed in 28.3 and the other in accordance
withas directed in 28.4.2.
28.2 Reagent Blank Solution—Carry a reagent blank through the entire procedure using the same amount of all reagents with
the sample omitted.
28.3 Color Development—Proceed with one of the 10-mL portions obtained in 28.1.2.2 or 28.1.3.2, in accordance withas
directed in 26.3.
28.4 Reference Solutions:
28.4.1 Water—Use this as the reference solution for the reagent blank solution.
28.4.2 Background Color Reference Solution—Add 15 mL of Na SO solution to the second 10-mL portion obtained in 28.1.2.2
2 3
or 28.1.3.2. 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
2 4
for the test solution.
28.5 Spectrophotometry—Take the spectrophotometric absorbance readings of the reagent blank solution and of the test solution
(using the respective reference solutions) in accordance withas directed in 26.5 or 27.5 depending upon the estimated composition
of phosphorus in the sample.
29. Calculation
29.1 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 3 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.
30. Precision and Bias
30.1 Precision—Nine laboratories cooperated in testing this method and obtained the data summarized in Table 2.
30.2 Bias—The accuracy of this test method exhibits a slight negative bias 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 Information—
Phosphorus—Molybdenum Blue—Spectrophotometric Method
Phos- Repeat- Repro-
phorus ability ducibil-
Test Specimen
Found, (R , ity (R ,
1 2
% E173) E173)
1. Cast iron 15Ni-2Cr-5Cu (NIST 115, 0.114 P) 0.107 0.013 0.014
2. Cast iron (NIST 5k, 0.263 P) 0.257 0.016 0.012
3. Cast iron (NIST 7g, 0.794 P) 0.779 0.020 0.053
E351 − 18
SULFUR BY THE GRAVIMETRIC METHOD
This test method, which consisted of Sections 30 through 36, was discontinued in 1988.
SULFUR BY THE COMBUSTION-IODATE TITRATION METHOD
This test method, which consisted of Sections 37 through 45, was discontinued in 2012.
SILICON BY THE GRAVIMETRIC METHOD
46. Scope
46.1 This method covers the determination of silicon in compositions from 0.1 % to 6.1 %.
46. Scope
46.1 This method covers the determination of silicon from 0.1 % to 6.1 %.
47. Summary of Test Method
47.1 After dissolution of the sample, silicic acid is dehydrated by fuming with H SO or HClO . The solution is filtered, and
2 4 4
the impure silica is ignited and weighed. The silica is then volatilized with HF. The residue is ignited and weighed; the loss in
weightmass represents silica.
48. Interferences
48.1 The elements ordinarily present do not interfere if their compositions are under the maximum limits shown in 1.1.
49. Reagents
49.1 The analyst should make certain ensure by analyzing blanks and other checks that possible silicon contamination of
reagents will not significantly bias the results.
49.2 Perchloric Acid: Acid (HClO ):
49.2.1 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 in accordance withas directed in 49.2.2 – 49.2.6.
49.2.2 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.
49.2.3 Add paper pulp and filter immediately, using lowashlow-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
2 4
(1 + 49). Transfer the papers to platinum crucibles.
49.2.4 Dry the papers and heat at 600 °C until the carbon is removed. Finally ignite at 1100 °C to 1150 °C or to constant
weightmass (at least 30 min). Cool in a desiccator and weigh.
49.2.5 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
2 4 2
a 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
49.2.6 Calculate the percent of silicon as follows:
Silicon,%5 @~A 2 B! 2 ~C 2 D!# 30.4674⁄E 3100 (3)
where:
A = initial weight of crucible plus impure SiO when 65 mL of HClO was taken, g,
2 4
B = final weight of crucible plus impurities when 65 mL of HClO was taken, g,
C = initial weight of crucible plus impure SiO when 15 mL of HClO was taken, g,
2 4
D = final weight of crucible plus impurities when 15 mL of HClO was taken, g, and
E = nominal weight (80 g) of 50 mL of HClO .
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
E351 − 18
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 .
49.3 Sodium Silicate Solution—Transfer 11.0 g of sodium silicate (Na SiO ·9H O) to a 400-mL beaker. Add 150 mL of water
2 3 2
and 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 .
49.4 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
49.5 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 pick
up absorb silicon.
50. Procedure
50.1 Select and weigh a sample in accordance with the following:as follows:
Sample Tolerance Dehydrating Acid, mL
Silicon, % Weight, g in Sample Dehydrating Acid, mL Tolerance
H SO Weight, mg Sample in Sample
2 4
(1 + 4) HClO Silicon, % Mass, g Mass,
0.10 to 1.00 4.0 4 150 60
1.00 to 2.00 3.0 3 100 50
2.00 to 4.00 2.0 2 100 40
4.00 to 6.00 1.0 1 100 40
Transfer it to a 400-mL beaker or a 300-mL porcelain casserole.
50.2 If the sample type is other than white iron, proceed as directed in 50.3; treat samples of white iron as directed in 50.2.1.
50.2.1 Crush the material in an iron mortar and use only particles passing through a No. 100 (150-μm)150-μm (No. 100) sieve.
Add 30 mL of HNO and 10 mL of HBr. When the dissolution reaction becomes passive, decant the bulk of the solution to a
400-mL beaker and crush the remaining insoluble matter in the original beaker with a glass rod. Add 20 mL of HNO and 10 mL
of HBr, and heat gently until dissolution is complete. Combine the two portions of the solution and add the amount of H SO or
2 4
HClO specified in 50.1.
50.2.2 SulfuricH SO Acid Dehydration:
2 4
50.2.2.1 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 in accordance withas directed in 50.4.
50.2.3 PerchloricHClO Acid Dehydration:
50.2.3.1 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.
50.3 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
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.
50.4 Add 15 mL of HNO to the filtrate, stir, and evaporate in accordance withas directed in either 50.2.2 or 50.2.3, depending
upon the dehydrating acid used. Filter immediately, using a low-ash, 9-cm-100-porosity filter paper, and wash in accordance withas
directed in 50.3.
50.5 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 weightmass (at least 30 min). Cool in a desiccator
and weigh.
50.6 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
51. Calculation
51.1 Calculate the percent of silicon as follows:
Silicon,%5 A 2 B 3 0.4674 ⁄C 3100 (4)
@~~ ! ! #
where:
A = initial weight of crucible and impure SiO , g,
A = initial mass of crucible and impure SiO , g,
E351 − 18
TABLE 3 Statistical Information—Silicon Information—Silicon—
Gravimetric Method
Repeat- Repro-
Silicon
ability ducibil-
Test Specimen Found,
(R , ity (R ,
1 2
%
E173) E173)
HClO Dehydration
1. Cast iron 1.2Ni-0.3Cr-0.8 Mo (NIST 1.36 0.02 0.02
107b, 1.35 Si)
2. Cast iron (NIST 4i, 1.45 Si) 1.45 0.04 0.05
3. Cast iron 1.07Ni-0.32Cr (NIST 82a, 2.08 0.04 0.05
2.07 Si)
4. Cast iron (NIST 5k, 2.08 Si) 2.08 0.03 0.05
5. Cast iron, high (0.79) phosphorus 2.40 0.04 0.07
(NIST 7g, 2.41 Si)
6. White cast iron (NIST 1176, 3.19 Si) 3.20 0.03 0.10
H SO Dehydration
2 4
1. Cast iron 1.2Ni-0.3Cr-0.8Mo (NIST 1.36 0.02 0.03
107b, 1.35 Si)
2. Cast iron (NIST 4i, 1.
...

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...