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ASTM E1728-03

(Practice)

Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination

Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination

SIGNIFICANCE AND USE
This practice is intended for the collection of settled dust samples in and around buildings and related structures for the subsequent determination of lead content in a manner consistent with that described in the HUD Guidelines4 and 40 CFR 745.63 (EPA 403 Rule). The practice is meant for use in the collection of settled dust samples that are of interest in clearance, hazard assessment, risk assessment, and other purposes.
Use of different pressures applied to the sampled surface along with the use of different wiping patterns contribute to collection variability. Thus, the sampling result can vary between operators performing collection from identical surfaces as a result of collection variables. Collection for any group of sampling locations at a given sampling site is best when limited to a single operator.
This practice is recommended for the collection of settled dust samples from hard, relatively smooth, nonporous surfaces. This practice is less effective for collecting settled dust samples from surfaces with substantial texture such as rough concrete, brickwork, textured ceilings, and soft fibrous surfaces such as upholstery and carpeting.
SCOPE
1.1 This practice covers the collection of settled dust on surfaces using the wipe sampling method. These samples are collected in a manner that will permit subsequent extraction and determination of lead using laboratory analysis techniques such as atomic spectrometry or electroanalysis.
1.2 This practice does not address the sampling design criteria (that is, sampling plan which includes the number and location of samples) that are used for clearance, lead hazard evaluation, risk assessment, and other purposes. To provide for valid conclusions, sufficient numbers of samples should be obtained as directed by a sampling plan.
1.3 This practice contains notes that are explanatory and are not part of the mandatory requirements of this practice.
1.4 The values stated in SI units are to be regarded as the standard.
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 and health practices and determine the applicability of regulatory limitations prior to use.

General Information

Status
Historical
Publication Date
30-Sep-2003
ICS
13.080.05 - Examination of soils in general
Technical Committee
E06 - Performance of Buildings
Current Stage
Ref Project

Relations

Replaces
ASTM E1728-02 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
Effective Date
01-Oct-2003
Replaced By
ASTM E1728-10 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
Effective Date
01-Oct-2010
Referred By
ASTM D7035-21 - Standard Test Method for Determination of Metals and Metalloids in Airborne Particulate Matter by Inductively Coupled Plasma Atomic Emission Spectrometry (ICP-AES)
Effective Date
01-Oct-2003
Referred By
ASTM D8344-20 - Standard Practice for Ammonium Bifluoride and Nitric Acid Digestion of Airborne Dust and Dust-Wipe Samples for the Determination of Metals and Metalloids
Effective Date
01-Oct-2003
Referred By
ASTM E1979-21 - Standard Practice for Ultrasonic Extraction of Paint, Dust, Soil, and Air Samples for Subsequent Determination of Lead
Effective Date
01-Oct-2003
Referred By
ASTM E3203-21 - Standard Test Method for Determination of Lead in Dried Paint, Soil, and Wipe Samples by Inductively Coupled Plasma-Optical Emission Spectroscopy (ICP-OES)
Effective Date
01-Oct-2003
Referred By
ASTM E1792-20 - Standard Specification for Wipe Sampling Materials for Lead in Surface Dust
Effective Date
01-Oct-2003
Referred By
ASTM D1356-20a - Standard Terminology Relating to Sampling and Analysis of Atmospheres
Effective Date
01-Oct-2003
Referred By
ASTM E3193-21 - Standard Test Method for Measurement of Lead (Pb) in Dust by Wipe, Paint, and Soil by Flame Atomic Absorption Spectrophotometry (FAAS)
Effective Date
01-Oct-2003
Referred By
ASTM E2913/E2913M-21 - Standard Practice for Hotplate Digestion of Lead from Composited Wipe Samples
Effective Date
01-Oct-2003
Referred By
ASTM E2914/E2914M-21 - Standard Practice for Ultrasonic Extraction of Lead from Composited Wipe Samples
Effective Date
01-Oct-2003
Referred By
ASTM E631-15 - Standard Terminology of Building Constructions
Effective Date
01-Oct-2003

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ASTM E1728-03 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead DeterminationASTM E1728-03 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
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ASTM E1728-03 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
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Standards Content (Sample)

NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.
Contact ASTM International (www.astm.org) for the latest information
Designation:E1728–03
Standard Practice for
Collection of Settled Dust Samples Using Wipe Sampling
1
Methods for Subsequent Lead Determination
This standard is issued under the fixed designation E1728; 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 E1613 Test Method for Determination of Lead by Induc-
tively Coupled Plasma Atomic Emission Spectrometry
1.1 This practice covers the collection of settled dust on
(ICP-AES), Flame Atomic Absorption Spectrometry
surfaces using the wipe sampling method. These samples are
(FAAS), or Graphite Furnace Atomic Absorption Spec-
collected in a manner that will permit subsequent extraction
trometry (GFAAS) Techniques
and determination of lead using laboratory analysis techniques
E1644 Practice for Hot Plate Digestion of Dust Wipe
such as atomic spectrometry or electroanalysis.
Samples for the Determination of Lead
1.2 This practice does not address the sampling design
E1792 Specification for Wipe Sampling Materials for Lead
criteria (that is, sampling plan which includes the number and
in Surface Dust
location of samples) that are used for clearance, lead hazard
E1979 Practice for Ultrasonic Extraction of Paint, Dust,
evaluation, risk assessment, and other purposes.To provide for
Soil, and Air Samples for Subsequent Determination of
valid conclusions, sufficient numbers of samples should be
Lead
obtained as directed by a sampling plan.
E2051 Practice for the Determination of Lead in Paint,
1.3 This practice contains notes that are explanatory and are
Settled Dust, Soil and Air Particulate by Field-Portable
not part of the mandatory requirements of this practice.
Electroanalysis
1.4 The values stated in SI units are to be regarded as the
2.2 Federal Regulations:
standard.
40 CFR 745.63, U.S. Environmental Protection Agency
1.5 This standard does not purport to address all of the
(EPA) “403 Rule:” Federal Register, Vol 66(4), 5 Jan.
safety concerns, if any, associated with its use. It is the
3
2001, p. 1206
responsibility of the user of this standard to establish appro-
priate safety and health practices and determine the applica-
3. Terminology
bility of regulatory limitations prior to use.
3.1 For definitions of terms not listed here, seeTerminology
2. Referenced Documents E1605.
2 3.2 Definitions:
2.1 ASTM Standards:
3.2.1 batch, n—a group of field or quality control (QC)
D4840 Guide for Sample Chain-of-Custody Procedures
samples that are collected or processed together at the same
E1605 Terminology Relating to Lead in Buildings
time using the same reagents and equipment.
3.2.2 sampling location, n—a specific area within a sam-
1
This practice is under the jurisdiction of ASTM Committee E06 on Perfor- pling site that is subjected to sample collection.
manceofBuildingsandisthedirectresponsibilityofSubcommitteeE06.23onLead
3.2.2.1 Discussion—Multiple sampling locations are com-
Hazards Associated with Buildings.
monly designated for a single sampling site (see 3.2.3).
Current edition approved Oct. 1, 2003. Published October 2003. Originally
3.2.3 sampling site, n—alocalgeographicareathatcontains
approved in 1994. Last previous edition approved in 2002 as E1728 – 02. DOI:
10.1520/E1728-03.
the sampling locations (see 3.2.2).
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contactASTM Customer Service at service@astm.org. ForAnnual Book ofASTM
3
Standards volume information, refer to the standard’s Document Summary page on Available from United States Environmental Protection Agency (EPA), Ariel
the ASTM website. Rios Bldg., 1200 Pennsylvania Ave., NW, Washington, DC 20460, www.epa.org.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1

---------------------- Page: 1 ----------------------
E1728–03
3.2.3.1 Discussion—A sampling site is generally limited to shaped,” and “L-shaped”) or templates of alternative areas
an area that is easily covered by walking. having accurately known dimensions (see Notes 1 and 2).
3.2.4 wipe, n—a disposable towellette that is moistened
NOTE 1—For most surfaces, it is recommended to collect settled dust
with a wetting agent. E1792 2
from a minimum of a 100 cm area to provide sufficient material for
5
3.2.4.1 Discussion—These towellettes are used to collect a
laboratory analysis. However, areas larger than 30 by 30 cm may be
sample of settled dust on a surface for subsequent lead appropriate for surfaces having little or no visible settled dust, and a
smaller sampling area may be appropriate for surfaces with very high
analysis.
levels o
...

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5.1 Bucket augers (Fig. 1) are relatively inexpensive, readily available, available in different types depending on the media to be sampled, and most can be easily operated by one person. They collect a reasonably cylindrical but disturbed sample of surface or subsurface soil or waste. They are generally not suited for sampling gravelly or coarser soil and are unsuitable for sampling rock. There are other designs of hand augers, such as the Edelman auger, used to retrieve difficult materials such as waste, sands, peat, and mud.
FIG. 1 Bucket Auger  
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ASTM
ASTM D6706-01(2021)(Test Method)
Standard Test Method for Measuring Geosynthetic Pullout Resistance in Soil

SIGNIFICANCE AND USE
5.1 The pullout test method is intended as a performance test to provide the user with a set of design values for the test conditions examined.  
5.1.1 The test method is applicable to all geosynthetics and all soils.  
5.1.2 This test method produces test data, which can be used in the design of geosynthetic-reinforced retaining walls, slopes, and embankments, or in other applications where resistance of a geosynthetic to pullout under simulated field conditions is important.  
5.1.3 The test results may also provide information related to the in-soil stress-strain response of a geosynthetic under confined loading conditions.  
5.2 The pullout resistance versus normal stress plot obtained from this test is a function of soil gradation, plasticity, as-placed dry unit weight, moisture content, length and surface characteristics of the geosynthetic, and other test parameters. Therefore, results are expressed in terms of the actual test conditions. The test measures the net effect of a combination of pullout mechanisms, which may vary depending on type of geosynthetic specimen, embedment length, relative opening size, soil type, displacement rate, normal stress, and other factors.  
5.3 Information between laboratories on precision is incomplete. In cases of dispute, comparative tests to determine if there is a statistical bias between laboratories may be advisable.
SCOPE
1.1 Resistance of a geosynthetic to pullout from soil is determined using a laboratory pullout box.  
1.2 The test method is intended to be a performance test conducted as closely as possible to replicate design or as-built conditions. It can also be used to compare different geosynthetics, soil types, etc., and thereby be used as a research and development test procedure.  
1.3 The values stated in SI units are to be regarded as standard. The values stated in parentheses are provided for information only.  
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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ASTM
ASTM D7351/D7351M-21(Test Method)
Standard Test Method for Determination of Sediment Retention Device (SRD) Effectiveness in Sheet Flow Applications

SIGNIFICANCE AND USE
5.1 This test method quantifies the effectiveness of a sediment retention device (SRD) by measuring the ability of the SRD to retain eroded sediments caused by sheet flowing water under full-scale conditions. This test method may also assist in identifying physical attributes of SRDs that contribute to their erosion control performance.  
5.2 The effectiveness of SRDs is installation dependent. Thus, replicating field installation techniques is an important aspect of this test method. This test method is full-scale and therefore, appropriate as an indication of product performance, for general comparison of product capabilities, and for assessment of product installation techniques.
Note 1: Test Method D5141 is an alternate test method for evaluating sediment retention device effectiveness, if it is not necessary to simulate field installation conditions.
Note 2: The quality of the result produced by this standard is dependent on the competence of the personnel performing it, and the suitability of the equipment and facilities used. Agencies that meet the criteria of Practice D3740 are generally considered capable of competent and objective testing/sampling/inspection/etc. Users of this standard are cautioned that compliance with Practice D3740 does not in itself assure reliable results. Reliable results depend on many factors: Practice D3740 provides a means of evaluating some of those factors.
SCOPE
1.1 This test method establishes the guidelines, requirements and procedures for evaluating the ability of Sediment Retention Devices (SRDs) to retain sediment when exposed to sediment-laden water “sheet” flows.  
1.2 This test method is applicable to the use of an SRD as a vertical permeable interceptor designed to remove suspended soil from overland, nonconcentrated water flow. The function of an SRD is to trap and allow settlement of soil particles from sediment laden water. The purpose is to reduce the transport of eroded soil from a disturbed site by water runoff.  
1.3 The test method presented herein is intended to indicate representative performance and is not necessarily adequate for all purposes in view of the wide variety of possible sediments and performance objectives.  
1.4 Units—The values stated in either SI units or inch-pound units [given in brackets] are to be regarded separately as standard. Only SI units are used in equations and appendixes. The values stated in each system may not be exact equivalents; therefore, each system shall be used independently of the other. Combining values from the two systems may result in nonconformance with the standard. Reporting of test results in units other than SI shall not be regarded as nonconformance with this standard.  
1.5 All observed and calculated values shall conform to the guidelines for significant digits and rounding established in Practice D6026.  
1.5.1 The procedures used to specify how data are collected/recorded and calculated in this standard are regarded as the industry standard. In addition, they are representative of the significant digits that should generally be retained. The procedures used do not consider material variation, purpose for obtaining the data, special purpose studies, or any consideration for the user’s objectives; and it is common practice to increase or reduce significant digits of reported data to commensurate with these considerations. It is beyond the scope of this standard to consider significant digits used in analysis methods for engineering design.  
1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.7 This international standard was developed in accordance with internationally recognized principles on standardization established...

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ASTM D5633-21(Practice)
Standard Practice for Sampling with a Scoop

SIGNIFICANCE AND USE
5.1 This practice is intended for use in collecting samples of contaminated soils and similar materials.  
5.2 Scoops are used primarily for collecting samples near the surface. Subsurface samples can be obtained by first removing higher layers using a shovel or other suitable equipment and collecting the sample with the scoop.  
5.3 Because of their simplicity, scoops are useful in taking samples of waste materials where decontamination or disposal is a problem with other types of sampling equipment. Scoops are also suitable for use in rapid screening programs, pilot studies, and other semi-quantitative investigations.  
5.4 Samples should be collected in accordance with an appropriate work plan (see Practice D5283 and Guide D4687).
SCOPE
1.1 This practice covers the method and equipment used to collect surface and near-surface samples of soils and physically similar materials using a scoop.  
1.2 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.  
1.3 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.

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