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ASTM E1792-03

(Specification)

Standard Specification for Wipe Sampling Materials for Lead in Surface Dust

Standard Specification for Wipe Sampling Materials for Lead in Surface Dust

ABSTRACT
This specification covers requirements for wipe sampling materials that are used to collect settled dusts on surfaces for the subsequent determination of lead. The wipes shall be tested for conformance to background lead, lead recoverability, collection efficiency, ruggedness which shall be determined using butted vinyl-composite floor tiles as a test surface, moisture content, coefficient of variation in mass, linear dimensions such as mean area and mean length, and mean thickness requirements.
SCOPE
1.1 This specification covers requirements for wipe materials that are used to collect settled dusts on hard surfaces for the subsequent determination of lead.  
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 and health practices and determine the applicability of regulatory limitations prior to use.

General Information

Status
Historical
Publication Date
30-Sep-2003
ICS
71.040.50 - Physicochemical methods of analysis
Technical Committee
E06 - Performance of Buildings
Current Stage
Ref Project

Relations

Replaces
ASTM E1792-02 - Standard Specification for Wipe Sampling Materials for Lead in Surface Dust
Effective Date
01-Oct-2003
Replaced By
ASTM E1792-03(2011) - Standard Specification for Wipe Sampling Materials for Lead in Surface Dust
Effective Date
01-Apr-2011
Referred By
ASTM E631-15 - Standard Terminology of Building Constructions
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 D7822-18 - Standard Practice for Dermal Wipe Sampling for the Subsequent Determination of Metals and Metalloids
Effective Date
01-Oct-2003
Referred By
ASTM E3074/E3074M-20 - Standard 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
Effective Date
01-Oct-2003
Referred By
ASTM D7659-21 - Standard Guide for Strategies for Surface Sampling of Metals and Metalloids for Worker Protection
Effective Date
01-Oct-2003
Referred By
ASTM E1775-20 - Standard Guide for Evaluating Performance of On-Site Extraction and Field-Portable Electrochemical or Spectrophotometric Analysis for Lead
Effective Date
01-Oct-2003
Referred By
ASTM D6785-20 - Standard Test Method for Determination of Lead in Workplace Air Using Flame or Graphite Furnace Atomic Absorption Spectrometry
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 E1644-21 - Standard Practice for Hot Plate Digestion of Dust Wipe Samples for the 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 E1605-22 - Standard Terminology Relating to Lead in Buildings
Effective Date
01-Oct-2003
Referred By
ASTM E1728/E1728M-20 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
Effective Date
01-Oct-2003
Referred By
ASTM E2271/E2271M-22 - Standard Practice for Clearance Examinations Following Lead Hazard Reduction Activities in Multifamily Dwellings
Effective Date
01-Oct-2003

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ASTM E1792-03 - Standard Specification for Wipe Sampling Materials for Lead in Surface DustASTM E1792-03 - Standard Specification for Wipe Sampling Materials for Lead in Surface Dust
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ASTM E1792-03 - Standard Specification for Wipe Sampling Materials for Lead in Surface Dust
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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: E1792 – 03
Standard Specification for
1
Wipe Sampling Materials for Lead in Surface Dust
This standard is issued under the fixed designation E1792; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope 3.2 Definitions:
3.2.1 lot, n—a finite quantity of a given product manufac-
1.1 Thisspecificationcoversrequirementsforwipesthatare
tured under production conditions that are considered uniform.
used to collect settled dusts on surfaces for the subsequent
3.2.2 shelf life, n—for dust-wiping sampling, the maximum
determination of lead.
timeintervalduringwhichawipecanbestoredinanunopened
1.2 This standard does not purport to address all of the
package and remain suitable for sampling of settled dust.
safety concerns, if any, associated with its use. It is the
3.2.3 vinyl-composite tile, n—a resilient floor covering
responsibility of the user of this standard to establish appro-
composed of binder, fillers, and pigments. The binder consists
priate safety and health practices and determine the applica-
of one or more resins of poly (vinyl chloride) or vinyl cholride
bility of regulatory limitations prior to use.
copolymers, or both, compounded with suitable plasticizers
2. Referenced Documents
and stabilizers. Other polymeric resins may be incorporated as
2
part of the binder (See Terminology F141).
2.1 ASTM Standards:
3.2.4 wipe, n—a disposable towellette that is moistened
E105 Practice for Probability Sampling of Materials
with a wetting agent.
E691 Practice for Conducting an Interlaboratory Study to
3.2.4.1 Discussion—The towellette is used to collect a
Determine the Precision of a Test Method
sample of settled dust on a surface for subsequent lead
E1605 Terminology Relating to Lead in Buildings
analysis.
E1613 Test Method for Determination of Lead by Induc-
tively Coupled Plasma Atomic Emission Spectrometry
4. Significance and Use
(ICP-AES), Flame Atomic Absorption Spectrometry
4.1 This specification is intended for use by manufacturers
(FAAS), or Graphite Furnace Atomic Absorption Spec-
and suppliers to evaluate the performance of wipe sampling
trometry (GFAAS) Techniques
materials for lead in surface dust.
E1644 Practice for Hot Plate Digestion of Dust Wipe
4.2 This specification may also be employed by users of
Samples for the Determination of Lead
wipes to compare the performance of candidate wipes for the
E1728 Practice for Collection of Settled Dust Samples
sampling of lead in surface dust.
Using Wipe Sampling Methods for Subsequent Lead
Determination
5. Manufacture
E2239 Practice for Record Keeping and Record Preserva-
5.1 The wipes shall be made from materials using methods
tion for Lead Hazard Activities
thatensurecompliancewiththerequirementsofSections6and
F141 Terminology Relating to Resilient Floor Coverings
8,andshallbecleanandfreeofimperfectionsthatwouldaffect
3. Terminology their performance.
3.1 For definitions of terms not listed here, seeTerminology
6. General Requirements
E1605.
6.1 Wipes shall conform to the requirements in Paragraphs
6.1.1 to 6.1.8. Test procedures for each requirement are found
1
This specification is under the jurisdiction of ASTM Committee E06 on
in Section 8.
Performance of Buildings and is the direct responsibility of Subcommittee E06.23
6.1.1 Background Lead—The mean background lead con-
on Lead Hazards Associated with Buildings.
tent per un-spiked wipes tested shall be less than 1.0 µg.
Current edition approved Oct. 1, 2003. Published October 2003. Originally
approved in 1996. Last previous edition approved in 2002 as E1792 – 02. DOI:
6.1.2 Lead Recoveries—The mean lead recoveries from
10.1520/E1792-03.
wipes spiked with Certified Reference Materials (CRMs)
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
having 20 µg, 100 µg, and 500 µg (610%) of lead per sample
contactASTM Customer Service at service@astm.org. ForAnnual Book ofASTM
shall be 100 % 6 20 % of the mean lead recovery from the
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.
1

---------------------- Page: 1 ----------------------
E1792 – 03
CRM alone, that is, without a wipe included in the analysis 8.2.2 Alternatively,manuallydistribute(4)aknownmassof
3
(1) . The coefficient of variation of the recoveries of samples lead-containing CRM uniformly onto the test surface, of
2
with lead levels of 20 µg shall not exceed 25 percent. The 900 cm minimum area, and then wipe the surface in accor-
coefficients
...

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4.4 PFAs History and Use:  
4.4.1 In the 1940s, industrial processes to co...
SCOPE
1.1 Per- and polyfluoroalkyl substances (PFAS) are a group of over 7,000 manmade compounds consisting of polymeric chains of carbon bonded to fluorine atoms, usually with a polar functional group at the head. This guide recognizes that PFAS can be categorized as polymeric or nonpolymeric, collectively amounting to more than 4,700 Chemical Abstracts Service (CAS)-registered substances. Environmental concerns pertaining to PFAS are centered primarily on the perfluoroalkyl acids (PFAA), a subclass of per-and polyfluoroalkyl substances, which display extreme persistence and chain-length dependent bioaccumulation and adverse effects in biota.  
1.2 The regulatory framework for PFAS continues to evolve, both domestically and internationally. The United States Environmental Protection Agency (EPA) is proceeding with a wide-ranging set of PFAS regulatory actions (EPA, 2021). While the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) does not currently recognize PFAS as hazardous substances, the statute does require actions to protect public health and the environment from contaminants and pollutants released to the environment. Other federal regulatory programs, such as the Safe Drinking Water Act are being used to address drinking water supplies adversely impacted by releases of PFAS. The Clean Water Act’s National Pollutant Discharge Elimination System (NPDES) permitting program is tool that both federal and state regulators are using to regulate the inflows of PFAS-impacted wastewaters at both publicly-owned treatment works (POTW) and federally-owned wastewater treatment plants and the concentration of PFAS in permitted effluent. EPA continues to add additional per-and polyfluoroalkyl substances to the list of substances reportable under the federal Toxic Release Inventory (TRI) reporting program. International efforts to address per-and polyfluoroalkyl substances include Australia’s PFAS Nation...

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  • Guide
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ASTM
ASTM G136-03(2023)e1(Practice)
Standard Practice for Determination of Soluble Residual Contaminants in Materials by Ultrasonic Extraction

SIGNIFICANCE AND USE
5.1 This practice is suitable for the determination of extractable substances that may be found in materials used in systems or components requiring a high level of cleanliness, such as oxygen systems. Soft goods, such as seals and valve seats, may be tested as received. Gloves and wipes, or samples thereof, to be used in cleaning operations may be evaluated prior to use to ensure that the proposed extracting agent does not extract or deposit chemicals, or both, on the surface to be cleaned.  
5.2 Wipes or other cleaning equipment may be tested after use to determine the amount of contaminant removed from a surface.
Note 1: The amount of material extracted may be dependent upon the frequency and power density of the ultrasonic unit.  
5.3 The extraction efficiency has been shown to vary with the frequency and power density of the ultrasonic unit. The unit, therefore, must be carefully evaluated to optimize the extraction conditions.
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1.1 This practice may be used to extract nonvolatile and semivolatile residues from materials such as new and used gloves, new and used wipes, component soft goods, and so forth. When used with proposed cleaning materials (wipes, gloves, and so forth), this practice may be used to determine the potential of the proposed solvent or other fluids to extract contaminants (plasticizers, residual detergents, brighteners, and so forth) and deposit them on the surface being cleaned.  
1.2 This practice is not suitable for the evaluation of particulate contamination.  
1.3 The values stated in SI units are to be regarded standard. No other units of measurement are included in this standard.  
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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