Standard Practice for Ultrasonic Extraction of Lead from Composited Wipe Samples

SIGNIFICANCE AND USE
5.1 This practice is for use in the preparation of no more than four wipe samples collected from equally-sized areas in the same space combined to form a composited sample for subsequent determination of lead content.  
5.2 This practice assumes use of wipes that meet Specification E1792 and should not be used unless the wipes meet Specification E1792.  
5.3 This practice is capable of preparing samples for determination of lead bound within paint dust.  
5.4 This practice may not be capable of preparing samples for determination of lead bound within silica or silicate matrices, or within matrices not soluble in nitric acid.  
5.5 Adjustment of the nitric acid concentration or acid strength, or both, of the final extract solution may be necessary for compatibility with the instrumental analysis method to be used for lead quantification.  
5.6 This sample preparation practice has not been validated for use and must be validated by the user prior to using the practice for client samples.
Note 1: Each combination of wipes (two wipes, three wipes, and four wipes) constitutes a different matrix and must be separately validated.
SCOPE
1.1 This practice covers the extraction of lead (Pb) using ultrasonication, heat and nitric acid from a composited sample of up to four individual wipe samples of settled dust collected from equally-sized areas in the same space.  
1.2 This practice contains notes which are explanatory and not part of mandatory requirements of the practice.  
1.3 This practice should be used by analysts experienced in digestion techniques such as hot blocks. Like all procedures used in an analytical laboratory, this practice needs to be validated for use and shown to produce acceptable results before being applied to client samples.  
1.4 The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each system are not necessarily exact equivalents; therefore, to ensure conformance with the standard, each system shall be used independently of the other, and values from the two systems shall not be combined.  
1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.6 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

General Information

Status
Published
Publication Date
31-Aug-2021
Technical Committee
D22 - Air Quality

Relations

Effective Date
01-Apr-2024
Effective Date
01-Apr-2024
Effective Date
01-Mar-2024
Effective Date
01-May-2020
Effective Date
15-Dec-2018
Effective Date
01-Nov-2018
Effective Date
01-Oct-2018
Effective Date
01-Sep-2018
Effective Date
01-Oct-2016
Effective Date
01-Jan-2016
Effective Date
01-Apr-2013
Effective Date
15-Jul-2012
Effective Date
15-Jul-2012
Effective Date
15-Jul-2012
Effective Date
01-Apr-2011

Overview

ASTM E2914/E2914M-21 is the standard practice for the ultrasonic extraction of lead from composited wipe samples. Published by ASTM International, this standard provides detailed procedures for extracting lead using ultrasonication, heat, and nitric acid from up to four individual wipe samples, which are composited from equally-sized areas within a single space. The aim is to prepare these samples for accurate determination of settled lead dust, which is crucial for lead hazard assessment and regulatory compliance in environments such as homes, schools, and workplaces.

This practice is particularly relevant for laboratories and professionals involved in environmental sample analysis, providing a recognized protocol for reliable and consistent sample preparation. The standard emphasizes proper validation of methods to ensure accuracy and highlights critical safety, health, and operational considerations.

Key Topics

  • Ultrasonic Extraction Technique: The use of ultrasonication, combined with heat and nitric acid, enhances the efficiency of lead extraction from dust collected on wipes.
  • Composited Wipe Sampling: Up to four wipe samples from equally-sized areas can be combined, providing a representative sample of larger spaces and reducing analytical load.
  • Lead Detection: The method is suitable for detecting lead contamination particularly in paint dust, facilitating lead exposure risk assessments.
  • Sample Matrix Limitations: The practice does not guarantee effective extraction of lead in silica or silicate matrices, or substances not soluble in nitric acid.
  • Validation Requirement: Each unique combination of wipes must be separately validated by the user, ensuring the method's fit for purpose in specific laboratory contexts.
  • Compatibility with Analytical Methods: Users may need to adjust nitric acid concentrations to accommodate different lead quantification techniques such as ICP-AES or electroanalytical methods.

Applications

  • Environmental Health and Safety: This standard is critical for agencies and professionals assessing lead contamination in buildings, especially after renovation, demolition, or suspected lead hazards.
  • Regulatory Compliance: Fulfilling requirements under 40 CFR Part 745 (Lead-Based Paint Poisoning Prevention), the method supports compliance with local and federal lead safety regulations.
  • Laboratory Analysis: Accredited laboratories use ASTM E2914/E2914M-21 to standardize lead extraction from dust, ensuring reliable and comparable results for clients.
  • Quality Assurance in Sampling: By compositing and extracting settled dust samples under controlled conditions, the standard aids in the documentation and traceability of sample processing and analysis.
  • Lead Hazard Reduction Projects: Post-remediation clearance examinations leverage these procedures to confirm that lead levels meet safety thresholds.

Related Standards

Implementing ASTM E2914/E2914M-21 is often accompanied by adherence to related ASTM and international standards, including:

  • ASTM E1792: Specification for Wipe Sampling Materials for Lead in Surface Dust (required for compliant wipes)
  • ASTM D6966 / E1728: Practices for the collection of settled dust samples using wipe sampling methods
  • ASTM E1613 / E2051: Test methods and practices for the determination of lead using atomic spectrometric and electroanalytical techniques
  • ASTM E2271/E2271M, E3074/E3074M: Practices for clearance examinations following lead hazard reduction activities
  • ISO/IEC 17025:2017: General requirements for the competence of testing and calibration laboratories.

Practical Value

ASTM E2914/E2914M-21 provides a validated, standardized method for preparing composite wipe samples for lead analysis, supporting reliable lead exposure assessments. Incorporating ultrasonic extraction ensures high recovery rates of lead from settled dust, and composited sampling optimizes laboratory workflows. By following this practice, laboratories, consultants, and regulators can confidently interpret lead contamination results, maintain compliance with environmental safety standards, and enhance public health protection. Proper implementation and documentation of this method bolster the credibility and traceability of lead hazard evaluation activities.

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Frequently Asked Questions

ASTM E2914/E2914M-21 is a standard published by ASTM International. Its full title is "Standard Practice for Ultrasonic Extraction of Lead from Composited Wipe Samples". This standard covers: SIGNIFICANCE AND USE 5.1 This practice is for use in the preparation of no more than four wipe samples collected from equally-sized areas in the same space combined to form a composited sample for subsequent determination of lead content. 5.2 This practice assumes use of wipes that meet Specification E1792 and should not be used unless the wipes meet Specification E1792. 5.3 This practice is capable of preparing samples for determination of lead bound within paint dust. 5.4 This practice may not be capable of preparing samples for determination of lead bound within silica or silicate matrices, or within matrices not soluble in nitric acid. 5.5 Adjustment of the nitric acid concentration or acid strength, or both, of the final extract solution may be necessary for compatibility with the instrumental analysis method to be used for lead quantification. 5.6 This sample preparation practice has not been validated for use and must be validated by the user prior to using the practice for client samples. Note 1: Each combination of wipes (two wipes, three wipes, and four wipes) constitutes a different matrix and must be separately validated. SCOPE 1.1 This practice covers the extraction of lead (Pb) using ultrasonication, heat and nitric acid from a composited sample of up to four individual wipe samples of settled dust collected from equally-sized areas in the same space. 1.2 This practice contains notes which are explanatory and not part of mandatory requirements of the practice. 1.3 This practice should be used by analysts experienced in digestion techniques such as hot blocks. Like all procedures used in an analytical laboratory, this practice needs to be validated for use and shown to produce acceptable results before being applied to client samples. 1.4 The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each system are not necessarily exact equivalents; therefore, to ensure conformance with the standard, each system shall be used independently of the other, and values from the two systems shall not be combined. 1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. 1.6 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

SIGNIFICANCE AND USE 5.1 This practice is for use in the preparation of no more than four wipe samples collected from equally-sized areas in the same space combined to form a composited sample for subsequent determination of lead content. 5.2 This practice assumes use of wipes that meet Specification E1792 and should not be used unless the wipes meet Specification E1792. 5.3 This practice is capable of preparing samples for determination of lead bound within paint dust. 5.4 This practice may not be capable of preparing samples for determination of lead bound within silica or silicate matrices, or within matrices not soluble in nitric acid. 5.5 Adjustment of the nitric acid concentration or acid strength, or both, of the final extract solution may be necessary for compatibility with the instrumental analysis method to be used for lead quantification. 5.6 This sample preparation practice has not been validated for use and must be validated by the user prior to using the practice for client samples. Note 1: Each combination of wipes (two wipes, three wipes, and four wipes) constitutes a different matrix and must be separately validated. SCOPE 1.1 This practice covers the extraction of lead (Pb) using ultrasonication, heat and nitric acid from a composited sample of up to four individual wipe samples of settled dust collected from equally-sized areas in the same space. 1.2 This practice contains notes which are explanatory and not part of mandatory requirements of the practice. 1.3 This practice should be used by analysts experienced in digestion techniques such as hot blocks. Like all procedures used in an analytical laboratory, this practice needs to be validated for use and shown to produce acceptable results before being applied to client samples. 1.4 The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each system are not necessarily exact equivalents; therefore, to ensure conformance with the standard, each system shall be used independently of the other, and values from the two systems shall not be combined. 1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. 1.6 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

ASTM E2914/E2914M-21 is classified under the following ICS (International Classification for Standards) categories: 13.040.99 - Other standards related to air quality; 71.040.50 - Physicochemical methods of analysis. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM E2914/E2914M-21 has the following relationships with other standards: It is inter standard links to ASTM E1792-24, ASTM E3074/E3074M-24, ASTM E2239-24, ASTM D1129-13(2020)e2, ASTM E1605-18b, ASTM D6966-18, ASTM E1605-18a, ASTM E1605-18, ASTM E1979-12(2016), ASTM E1728-16, ASTM D6966-13, ASTM E1605-04(2012), ASTM E1979-12, ASTM E2239-12, ASTM E1792-03(2011). Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM E2914/E2914M-21 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: E2914/E2914M − 21
Standard Practice for
Ultrasonic Extraction of Lead from Composited Wipe
Samples
ThisstandardisissuedunderthefixeddesignationE2914/E2914M;thenumberimmediatelyfollowingthedesignationindicatestheyear
of original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval.
A superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope 2. Referenced Documents
2.1 ASTM Standards:
1.1 This practice covers the extraction of lead (Pb) using
D1129 Terminology Relating to Water
ultrasonication, heat and nitric acid from a composited sample
D1193 Specification for Reagent Water
of up to four individual wipe samples of settled dust collected
D6966 Practice for Collection of Settled Dust Samples
from equally-sized areas in the same space.
Using Wipe Sampling Methods for Subsequent Determi-
1.2 This practice contains notes which are explanatory and
nation of Metals
not part of mandatory requirements of the practice.
E1605 Terminology Relating to Lead in Buildings
E1613 Test Method for Determination of Lead by Induc-
1.3 This practice should be used by analysts experienced in
tively Coupled Plasma Atomic Emission Spectrometry
digestion techniques such as hot blocks. Like all procedures
(ICP-AES), Flame Atomic Absorption Spectrometry
used in an analytical laboratory, this practice needs to be
(FAAS), or Graphite Furnace Atomic Absorption Spec-
validated for use and shown to produce acceptable results 3
trometry (GFAAS) Techniques (Withdrawn 2021)
before being applied to client samples.
E1728 PracticeforCollectionofSettledDustSamplesUsing
Wipe Sampling Methods for Subsequent Lead Determi-
1.4 The values stated in either SI units or inch-pound units
nation
are to be regarded separately as standard. The values stated in
E1792 Specification for Wipe Sampling Materials for Lead
each system are not necessarily exact equivalents; therefore, to
in Surface Dust
ensure conformance with the standard, each system shall be
E1979 Practice for Ultrasonic Extraction of Paint, Dust,
used independently of the other, and values from the two
Soil, and Air Samples for Subsequent Determination of
systems shall not be combined.
Lead
1.5 This standard does not purport to address all of the
E2051 Practice for the Determination of Lead in Paint,
safety concerns, if any, associated with its use. It is the
Settled Dust, Soil and Air Particulate by Field-Portable
responsibility of the user of this standard to establish appro-
Electroanalysis (Withdrawn 2010)
priate safety, health, and environmental practices and deter-
E2239 PracticeforRecordKeepingandRecordPreservation
mine the applicability of regulatory limitations prior to use.
for Lead Hazard Activities
E2271/E2271M Practice for Clearance Examinations Fol-
1.6 This international standard was developed in accor-
dance with internationally recognized principles on standard- lowing Lead Hazard Reduction Activities in Multifamily
Dwellings
ization established in the Decision on Principles for the
E3074/E3074M Practice for Clearance Examinations Fol-
Development of International Standards, Guides and Recom-
lowing Lead Hazard Reduction Activities in Single Fam-
mendations issued by the World Trade Organization Technical
ily Dwellings, in Individual Units of Multifamily
Barriers to Trade (TBT) Committee.
Dwellings, and in Other Child-Occupied Facilities
1 2
This practice is under the jurisdiction ofASTM Committee D22 on Air Quality For referenced ASTM standards, visit the ASTM website, www.astm.org, or
and is the direct responsibility of Subcommittee D22.12 on Sampling and Analysis contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
of Lead for Exposure and Risk Assessment. Standards volume information, refer to the standard’s Document Summary page on
Current edition approved Sept. 1, 2021. Published October 2021. Originally the ASTM website.
approved in 2014. Last previous edition approved in 2019 as E2914 – 19. DOI: The last approved version of this historical standard is referenced on
10.1520/E2914_E2914M-21. www.astm.org.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E2914/E2914M − 21
2.2 ISO Standards: 5.2 This practice assumes use of wipes that meet Specifica-
ISO 3585 Borosilicate glass 3.3 – Properties – Third edition tion E1792 and should not be used unless the wipes meet
ISO/IEC 17025:2017 General requirements for the compe- Specification E1792.
tence of testing and calibration laboratories
5.3 This practice is capable of preparing samples for deter-
2.3 Other Document:
mination of lead bound within paint dust.
40 CFR Part 745 Lead-Based Paint Poisoning Prevention in
5.4 This practice may not be capable of preparing samples
Certain Residential Structures
for determination of lead bound within silica or silicate
3. Terminology matrices, or within matrices not soluble in nitric acid.
3.1 For definitions of terms not appearing here, refer to
5.5 Adjustment of the nitric acid concentration or acid
Terminology D1129, Specification D1193, and Terminology strength, or both, of the final extract solution may be necessary
E1605.
for compatibility with the instrumental analysis method to be
used for lead quantification.
3.2 Definitions of Terms Specific to This Standard:
3.2.1 composited sample, n—the single sample resulting
5.6 This sample preparation practice has not been validated
from the combination of individual samples collected from
for use and must be validated by the user prior to using the
different sections of the same area.
practice for client samples.
NOTE 1—Each combination of wipes (two wipes, three wipes, and four
3.2.2 validation, n—provision of objective evidence that a
wipes) constitutes a different matrix and must be separately validated.
given item fulfills specified requirements, where the specified
requirements are adequate for an intended use.
6. Apparatus and Materials
ISO/IEC 17025:2017
6.1 Borosilicate Glass (conforming to ISO 3585) or Plastic
3.2.2.1 Discussion—The laboratory is responsible for vali-
Labware:
dating (1-4) non-standard methods, laboratory-designed/
6.1.1 Bottles, 125 mL, polypropylene or equivalent, with
developed methods, standard methods used outside their in-
screw caps, or equivalent,
tended scope, and amplifications and modifications of standard
6.1.2 Graduated Cylinders, 100 mL, and,
methods to confirm that the methods are fit for the intended
6.1.3 Stirring Rods, sized to reach the bottom of the bottles.
use.Thevalidationshallbeasextensiveasisnecessarytomeet
6.2 Tweezers, non-metallic tweezers sized to remove wipes
the needs of the given application or field of application. The
from sample shipping containers.
laboratory shall record the results obtained, the procedure used
for the validation, and a statement as to whether the method is
6.3 Ultrasonic Bath, 53 watts or greater output, 1 L or
fit for the intended use.
greater capacity, capable of heating to at least 60 °C.
3.2.2.2 Discussion—It is the responsibility of the laboratory
6.4 Thermometer, calibrated, non-mercury thermometer that
to carry out its testing activities in such a way as to satisfy the
covers the range from 0 °C to at least 110 °C.
needsoftheclient,theregulatoryauthorities,andorganizations
6.5 Disposable Plastic Gloves, impermeable and powder
providing recognition.
free, to avoid the possibility of contamination, and to protect
4. Summary of Practice
from contact with toxic and corrosive substances.
4.1 Up to four wipes, meeting the requirements of Specifi-
6.6 Pencil, with graphite tip.
cation E1792, are used according to Practices D6966 or E1728
6.7 Aluminum Foil.
to collect settled dust from equally-sized areas in the same
6.8 Surfactant, liquid.
space and composited as one sample as in Practices E2271/
E2271M and E3074/E3074M. This composited sample is then
7. Reagents
extracted using ultrasonication, heat and nitric acid. The
resulting extract solution is analyzed according to Test Method
7.1 Purity of Reagents—Reagent grade chemicals shall be
E1613 or Practice E2051.
used in all tests. Unless otherwise indicated, it is intended that
all reagents shall conform to the specifications of the Commit-
5. Significance and Use
tee onAnalytical Reagents of theAmerican Chemical Society,
5.1 This practice is for use in the preparation of no more
where such specifications are available (5). Other grades may
than four wipe samples collected from equally-sized areas in
be used provided that it can be demonstrated that they are of
the same space combined to form a composited sample for
sufficiently high purity to permit their use without decreasing
subsequent determination of lead content.
the accuracy of the determinations.
7.2 Reagent Water—Unless otherwise indicated, reference
Available from International Organization for Standardization (ISO), ISO
to water shall be understood to mean Type II reagent water
Central Secretariat, BIBC II, Chemin de Blandonnet 8, CP 401, 1214 Vernier,
conforming to Specification D1193.
Geneva, Switzerland, http://www.iso.org.
Available from U.S. Government Printing Office (GPO), 732 N. Capitol St.,
7.3 Nitric Acid:
NW, Washington, DC 20401, http://www.gpo.gov.
6 7.3.1 Concentrated, of suitable purity for atomic spectro-
The boldface numbers in parentheses refer to a list of references at the end of
this standard. metric analysis, such as spectroscopic grade.
E2914/E2914M − 21
NOTE 2—Suitable purity means having undetectable lead content in the purchased or constructed to allow for the regular and orderly placement of
extracted composited sample blanks. multiple bottles in the sonicator bath.
7.3.2 Dilute 35 % (v/v). Prepare by first adding 500 mL of
8.2.6 Preheat water in the sonicator bath to at least 60 °C.
reagent water toa1L volumetric flask and then carefully
8.2.7 Place the bottle (containing the wipes immersed in
adding 350 mL concentrated nitric acid. Make to volume with
dilute acid) upright in the sonicator bath, and ensure that the
reagent water.
w
...


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: E2914/E2914M − 19 E2914/E2914M − 21
Standard Practice for
Ultrasonic Extraction of Lead from Composited Wipe
Samples
This standard is issued under the fixed designation E2914/E2914M; the number immediately following the designation indicates the year
of original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval.
A superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope
1.1 This practice covers the extraction of lead (Pb) using ultrasonication, heat and nitric acid from a composited sample of up to
four individual wipe samples of settled dust collected from equally-sized areas in the same space.
1.2 This practice contains notes which are explanatory and not part of mandatory requirements of the practice.
1.3 This practice should be used by analysts experienced in digestion techniques such as hot blocks. Like all procedures used in
an analytical laboratory, this practice needs to be validated for use and shown to produce acceptable results before being applied
to client samples.
1.4 The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each
system are not necessarily exact equivalents; therefore, to ensure conformance with the standard, each system shall be used
independently of the other, and values from the two systems shall not be combined.
1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of
regulatory limitations prior to use.
1.6 This international standard was developed in accordance with internationally recognized principles on standardization
established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued
by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
2. Referenced Documents
2.1 ASTM Standards:
D1129 Terminology Relating to Water
D1193 Specification for Reagent Water
D6966 Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Determination of Metals
E631 Terminology of Building Constructions
E1605 Terminology Relating to Lead in Buildings
E1613 Test Method for Determination of Lead by Inductively Coupled Plasma Atomic Emission Spectrometry (ICP-AES),
This practice is under the jurisdiction of ASTM Committee D22 on Air Quality and is the direct responsibility of Subcommittee D22.12 on Sampling and
Analysis,Analysis of Lead,Lead for Exposure and Risk Assessment.
Current edition approved Jan. 1, 2019Sept. 1, 2021. Published February 2019October 2021. Originally approved in 2014. Last previous edition approved in 20142019 as
E2914–14. DOI: 10.1520/E2914_E2914M–19. – 19. DOI: 10.1520/E2914_E2914M-21.
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.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E2914/E2914M − 21
Flame Atomic Absorption Spectrometry (FAAS), or Graphite Furnace Atomic Absorption Spectrometry (GFAAS) Techniques
(Withdrawn 2021)
E1728 Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
E1792 Specification for Wipe Sampling Materials for Lead in Surface Dust
E1979 Practice for Ultrasonic Extraction of Paint, Dust, Soil, and Air Samples for Subsequent Determination of Lead
E2051 Practice for the Determination of Lead in Paint, Settled Dust, Soil and Air Particulate by Field-Portable Electroanalysis
(Withdrawn 2010)
E2239 Practice for Record Keeping and Record Preservation for Lead Hazard Activities
E2271/E2271M Practice for Clearance Examinations Following Lead Hazard Reduction Activities in Multifamily Dwellings
E3074/E3074M Practice for Clearance Examinations Following Lead Hazard Reduction Activities in Single Family Dwellings,
in Individual Units of Multifamily Dwellings, and in Other Child-Occupied Facilities
2.2 ISO Standards:
ISO 3585 Borosilicate Glassglass 3.3 – Properties – Third Editionedition
ISO/IEC 17025:2017 General Requirementsrequirements for the Competencecompetence of Testingtesting and Calibration
Laboratoriescalibration laboratories
2.3 Other Document:
40 CFR Part 745 Lead-Based Paint Poisoning Prevention in Certain Residential Structures
3. Terminology
3.1 For definitions of terms not appearing here, refer to Terminology D1129, Specification D1193, and Terminology E1605.
3.2 Definitions of Terms Specific to This Standard:
3.2.1 composited sample, n—the single sample resulting from the combination of individual samples collected from different
sections of the same area.
3.2.2 validation, n—provision of objective evidence that a given item fulfills specified requirements, where the specified
requirements are adequate for an intended use.
ISOISO/IEC 17025:2017
3.2.2.1 Discussion—
The laboratory is responsible for validating (1-4) non-standard methods, laboratory-designed/developed methods, standard
methods used outside their intended scope, and amplifications and modifications of standard methods to confirm that the methods
are fit for the intended use. The validation shall be as extensive as is necessary to meet the needs of the given application or field
of application. The laboratory shall record the results obtained, the procedure used for the validation, and a statement as to whether
the method is fit for the intended use.
3.2.2.2 Discussion—
It is the responsibility of the laboratory to carry out its testing activities in such a way as to satisfy the needs of the client, the
regulatory authorities, and organizations providing recognition.
3.2.3 The laboratory is responsible for validating (1-4) non-standard methods, laboratory-designed/developed methods, standard
methods used outside their intended scope, and amplifications and modifications of standard methods to confirm that the methods
are fit for the intended use. The validation shall be as extensive as is necessary to meet the needs of the given application or field
of application. The laboratory shall record the results obtained, the procedure used for the validation, and a statement as to whether
the method is fit for the intended use.
NOTE 1—It is the responsibility of the laboratory to carry out its testing activities in such a way as to satisfy the needs of the client, the regulatory
authorities, and organizations providing recognition.
4. Summary of Practice
4.1 Up to four wipes, meeting the requirements of Specification E1792, are used according to Practices D6966 or E1728 to collect
settled dust from equally-sized areas in the same space and composited as one sample as in Practices E2271/E2271M and
The last approved version of this historical standard is referenced on www.astm.org.
Available from International Organization for Standardization (ISO), ISO Central Secretariat, BIBC II, Chemin de Blandonnet 8, CP 401, 1214 Vernier, Geneva,
Switzerland, http://www.iso.org.
Available from U.S. Government Printing Office (GPO), 732 N. Capitol St., NW, Washington, DC 20401, http://www.gpo.gov.
The boldface numbers in parentheses refer to a list of references at the end of this standard.
E2914/E2914M − 21
E3074/E3074M. This composited sample is then extracted using ultrasonication, heat and nitric acid. The resulting extract solution
is analyzed according to Test Method E1613 or Practice E2051.
5. Significance and Use
5.1 This practice is for use in the preparation of no more than four wipe samples collected from equally-sized areas in the same
space combined to form a composited sample for subsequent determination of lead content.
5.2 This practice assumes use of wipes that meet Specification E1792 and should not be used unless the wipes meet Specification
E1792.
5.3 This practice is capable of preparing samples for determination of lead bound within paint dust.
5.4 This practice may not be capable of preparing samples for determination of lead bound within silica or silicate matrices, or
within matrices not soluble in nitric acid.
5.5 Adjustment of the nitric acid concentration or acid strength, or both, of the final extract solution may be necessary for
compatibility with the instrumental analysis method to be used for lead quantification.
5.6 This sample preparation practice has not been validated for use and must be validated by the user prior to using the practice
for client samples.
NOTE 1—Each combination of wipes (two wipes, three wipes, and four wipes) constitutes a different matrix and must be separately validated.
6. Apparatus and Materials
6.1 Borosilicate Glass (conforming to ISO 3585) or Plastic Labware:
6.1.1 Bottles, 125 mL, polypropylene or equivalent, with screw caps, or equivalent,
6.1.2 Graduated Cylinders, 100 mL, and,
6.1.3 Stirring Rods, sized to reach the bottom of the bottles.
6.2 Tweezers, non-metallic tweezers sized to remove wipes from sample shipping containers.
6.3 Ultrasonic Bath, 53 watts or greater output, 1 L or greater capacity, capable of heating to at least 60 °C.
6.4 Thermometer, calibrated, non-mercury thermometer that covers the range from 0 °C to at least 110 °C.
6.5 Disposable Plastic Gloves, impermeable and powder free, to avoid the possibility of contamination, and to protect from
contact with toxic and corrosive substances.
6.6 Pencil, with graphite tip.
6.7 Aluminum Foil.
6.8 Surfactant, liquid.
7. Reagents
7.1 Purity of Reagents—Reagent grade chemicals shall be used in all tests. Unless otherwise indicated, it is intended that all
reagents shall conform to the specifications of the Committee on Analytical Reagents of the American Chemical Society, where
such specifications are available (5). Other grades may be used provided that it can be demonstrated that they are of sufficiently
high purity to permit their use without decreasing the accuracy of the determinations.
E2914/E2914M − 21
7.2 Reagent Water—Unless otherwise indicated, reference to water shall be understood to mean Type II reagent water conforming
to Specification D1193.
7.3 Nitric Acid:
7.3.1 Concentrated, of suitable purity for atomic spectrometric analysis, such as spectroscopic grade.
E2914/E2914M − 21
NOTE 2—Suitable purity means having
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