Standard Practice for Hot Plate Digestion of Dust Wipe Samples for the Determination of Lead

SIGNIFICANCE AND USE
This practice is intended for the digestion of lead in dust wipe samples collected during various lead hazard activities performed in and around buildings and related structures.
This practice is also intended for the digestion of lead in dust wipe samples collected during and after building renovations.
This practice is applicable to the digestion of dust wipe samples that have or have not been collected in accordance with Practice E 1728 using wipes that may or may not conform to Specification E 1792.
This practice is applicable to the digestion of dust wipe samples that were placed in either hard-walled, rigid containers such as 50-mL centrifuge tubes or flexible plastic bags.
Note 2—Due to the difficulty in performing quantitative transfers of some samples from plastic bags, hard-walled rigid containers such as 50-mL plastic centrifuge tubes are recommended for sample collection.
Digestates prepared according to this practice are intended to be analyzed for lead concentration using spectrometric techniques such as Inductively Coupled Plasma Atomic Emission Spectrometry (ICP-AES) and Flame Atomic Absorption Spectrometry (FAAS) (see Test Method E 1613), or using electrochemical techniques such as anodic stripping voltammetry (see Practice E 2051).
This practice is not capable of determining lead bound within matrices, such as silica, that are not soluble in nitric acid.
This practice is capable of determining lead bound within paint.
SCOPE
1.1 This practice covers the acid digestion of surface dust samples (collected using wipe sampling practices) and associated quality control (QC) samples for the determination of lead.
1.2 The values stated in SI units are to be regarded as the standard.
1.3 This practice contains notes which are explanatory and not part of mandatory requirements of the 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 and health practices and determine the applicability of regulatory limitations prior to use.

General Information

Status
Historical
Publication Date
31-Jul-2004
Technical Committee
Current Stage
Ref Project

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NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.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:E1644–04
Standard Practice for
Hot Plate Digestion of Dust Wipe Samples for the
1
Determination of Lead
This standard is issued under the fixed designation E1644; 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 Settled Dust, Soil and Air Particulate by Field-Portable
Electroanalysis
1.1 This practice covers the acid digestion of surface dust
E2239 Practice for Record Keeping and Record Preserva-
samples (collected using wipe sampling practices) and associ-
tion for Lead Hazard Activities
ated quality control (QC) samples for the determination of
2.2 Other Documents:
lead.
EPASW 846, Method 3050, “Acid Digestion of Sediments,
1.2 The values stated in SI units are to be regarded as the
Sludges, and Soils.”This method is found in Test Methods
standard.
for Evaluating Solid Waste, Physical/Chemical Methods,
1.3 This practice contains notes which are explanatory and
3
U.S. EPA SW 846, 3rd Edition, Revision 1, 1987
not part of mandatory requirements of the standard.
NIOSH Manual of Analytical Methods, NIOSH 7082 and
1.4 This standard does not purport to address all of the
3
7105, Eller, P.M., Ed., 3rd ed., 1984
safety concerns, if any, associated with its use. It is the
responsibility of the user of this standard to establish appro-
3. Terminology
priate safety and health practices and determine the applica-
3.1 Definitions—For definitions of terms not appearing
bility of regulatory limitations prior to use.
here, refer to Terminologies D1129 and E1605.
2. Referenced Documents 3.2 Definitions of Terms Specific to This Standard:
2
3.2.1 blank wipe—an unused, unspiked dust wipe that is
2.1 ASTM Standards:
only removed from its packaging immediately before use.
D1129 Terminology Relating to Water
3.2.1.1 Discussion—Blank wipes are used to prepare non-
D1193 Specification for Reagent Water
spiked,spiked,andspikedduplicatequalityassurancesamples.
E1605 Terminology Relating to Lead in Buildings
3.2.2 dust wipe sample—surface dust collected on a wipe.
E1613 Test Method for Determination of Lead by Induc-
3.2.3 method blank—a digestate that reflects the maximum
tively Coupled Plasma Atomic Emission Spectrometry
treatment given any one sample within a sample batch except
(ICP-AES), Flame Atomic Absorption Spectrometry
that only the sampling medium (such as a blank wipe) is
(FAAS), or Graphite Furnace Atomic Absorption Spec-
initially placed into the digestion vessel. (The same reagents
trometry (GFAAS) Techniques
and processing conditions that are applied to field samples
E1724 Guide for Testing and Certification of Metal, Ore,
within a batch are also applied to the method blanks.)
and Metal-Related Reference Materials
3.2.3.1 Discussion—Analysis results from method blanks
E1728 Practice for Collection of Settled Dust Samples
provide information on the level of potential contamination
Using Wipe Sampling Methods for Subsequent Lead
resulting from the laboratory and sampling medium sources
Determination
that are experienced by samples processed within the batch.
E1792 Specification for Wipe Sampling Materials for Lead
3.2.4 non-spiked sample—a portion of a homogenized
in Surface Dust
sample that was targeted for the addition of analyte but is not
E2051 Practice for the Determination of Lead in Paint,
fortified with the target analytes before sample preparation.
3.2.4.1 Discussion—For wipe samples, a non-spiked
sample is equivalent to a method blank. Analysis results for
1
This practice is under the jurisdiction of ASTM Committee E06 on Perfor-
this sample are used to correct for background levels in the
manceofBuildingsandisthedirectresponsibilityofSubcommitteeE06.23onLead
blank wipes used for spiked and spiked duplicate samples.
Hazards Associated with Buildings.
Current edition approved August 1, 2004. Published August 2004. Originally
3.2.5 reagent blank—a digestate that reflects the maximum
approved in 1994. Last previous edition approved in 1998 as E1644 – 98. DOI:
treatment given any one sample within a sample batch except
10.1520/E1644-04.
2
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
3
Standards volume information, refer to the standard’s Document Summary page on Available from National Technical Information Service (NTIS), U.S. Depart-
the ASTM website. ment of Commerce, 5285 Port Royal Rd., Springfield, VA 22161.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
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