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ASTM D6281-04

(Test Method)

Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)

Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)

SCOPE
1.1 This test method is an analytical procedure using transmission electron microscopy (TEM) for the determination of the concentration of asbestos structures in ambient atmospheres and includes measurement of the dimension of structures and of the asbestos fibers found in the structures from which aspect ratios are calculated.
1.1.1 This test method allows determination of the type(s) of asbestos fibers present.
1.1.2 This test method cannot always discriminate between individual fibers of the asbestos and non-asbestos analogues of the same amphibole mineral.
1.2 This test method is suitable for determination of asbestos in both ambient (outdoor) and building atmospheres.
1.2.1 This test method is defined for polycarbonate capillary-pore filters or cellulose ester (either mixed esters of cellulose or cellulose nitrate) filters through which a known volume of air has been drawn and for blank filters.
1.3 The upper range of concentrations that can be determined by this test method is 7000 s/mm2. The air concentration represented by this value is a function of the volume of air sampled.
1.3.1 There is no lower limit to the dimensions of asbestos fibers that can be detected. In practice, microscopists vary in their ability to detect very small asbestos fibers. Therefore, a minimum length of 0.5 m has been defined as the shortest fiber to be incorporated in the reported results.
1.4 The direct analytical method cannot be used if the general particulate matter loading of the sample collection filter as analyzed exceeds approximately 10 % coverage of the collection filter by particulate matter.
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-Mar-2004
ICS
13.040.01 - Air quality in general
Technical Committee
D22 - Air Quality
Drafting Committee
D22.07 - Sampling, Analysis, Management of Asbestos, and Other Microscopic Particles
Current Stage
Ref Project

Relations

Replaces
ASTM D6281-98 - Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)
Effective Date
01-Apr-2004
Replaced By
ASTM D6281-06 - Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)
Effective Date
01-Apr-2006
Referred By
ASTM D6620-19 - Standard Practice for Asbestos Detection Limit Based on Counts
Effective Date
01-Apr-2004
Referred By
ASTM D7521-22 - Standard Test Method for Determination of Asbestos in Soil
Effective Date
01-Apr-2004
Referred By
ASTM D7201-06(2020) - Standard Practice for Sampling and Counting Airborne Fibers, Including Asbestos Fibers, in the Workplace, by Phase Contrast Microscopy (with an Option of Transmission Electron Microscopy)
Effective Date
01-Apr-2004
Referred By
ASTM D8526-23 - Standard Test Method for Analytical Procedure Using Transmission Electron Microscopy for the Determination of the Concentration of Carbon Nanotubes and Carbon Nanotube-containing Particles in Ambient Atmospheres
Effective Date
01-Apr-2004
Referred By
ASTM D7712-18 - Standard Terminology for Sampling and Analysis of Asbestos
Effective Date
01-Apr-2004

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ASTM D6281-04 - Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)ASTM D6281-04 - Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)
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ASTM D6281-04 - Standard Test Method for Airborne Asbestos Concentration in Ambient and Indoor Atmospheres as Determined by Transmission Electron Microscopy Direct Transfer (TEM)
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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: D 6281 – 04
Standard Test Method for
Airborne Asbestos Concentration in Ambient and Indoor
Atmospheres as Determined by Transmission Electron
1
Microscopy Direct Transfer (TEM)
This standard is issued under the fixed designation D6281; 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 (e) indicates an editorial change since the last revision or reapproval.
1. Scope responsibility of the user of this standard to establish appro-
2 priate safety and health practices and determine the applica-
1.1 This test method is an analytical procedure using
bility of regulatory limitations prior to use.
transmissionelectronmicroscopy(TEM)forthedetermination
of the concentration of asbestos structures in ambient atmo-
2. Referenced Documents
spheres and includes measurement of the dimension of struc-
3
2.1 ASTM Standards:
tures and of the asbestos fibers found in the structures from
D1193 Specification for Reagent Water
which aspect ratios are calculated.
D1356 Terminology Relating to Sampling andAnalysis of
1.1.1 This test method allows determination of the type(s)
Atmospheres
of asbestos fibers present.
D1357 Practice for Planning the Sampling of theAmbient
1.1.2 This test method cannot always discriminate between
Atmosphere
individualfibersoftheasbestosandnon-asbestosanaloguesof
4
2.2 ISO Standard:
the same amphibole mineral.
ISO 10312 Ambient air - Determination of asbestos fibres -
1.2 This test method is suitable for determination of asbes-
Direct-transfer transmission electron microscopy method
tos in both ambient (outdoor) and building atmospheres.
1.2.1 This test method is defined for polycarbonate
3. Terminology
capillary-pore filters or cellulose ester (either mixed esters of
3.1 Fordefinitionsofgeneraltermsusedinthistestmethod,
cellulose or cellulose nitrate) filters through which a known
refer to Terminology D1356 (see 2.1).
volume of air has been drawn and for blank filters.
3.2 Definitions of Terms Specific to This Standard:
1.3 The upper range of concentrations that can be deter-
2 3.2.1 acicular—the shape shown by an extremely slender
minedbythistestmethodis7000s/mm .Theairconcentration
crystal with cross-sectional dimensions that are small relative
represented by this value is a function of the volume of air
to its length, that is, needle-like.
sampled.
3.2.2 amphibole—a group of more than 60 different silicate
1.3.1 There is no lower limit to the dimensions of asbestos
minerals with similar crystal structures and complex composi-
fibers that can be detected. In practice, microscopists vary in
tions that conform to the nominal formula:
their ability to detect very small asbestos fibers. Therefore, a
A B C T O ~OH,F,Cl! (1)
minimum length of 0.5 µm has been defined as the shortest
0–1 2 5 8 22 2
fiber to be incorporated in the reported results.
where:
1.4 The direct analytical method cannot be used if the
A = K, Na, Ca,
generalparticulatematterloadingofthesamplecollectionfilter
2+
B =Fe , Mn, Mg, Ca, Na,
as analyzed exceeds approximately 10% coverage of the 3+ 2+
C = Al, Cr, Ti, Fe , Mg, Fe , Mn, and
collection filter by particulate matter. 3+
T = Si, Al, Cr, Fe ,Ti.
1.5 This standard does not purport to address all of the
In some varieties of amphibole, these elements can be
safety concerns, if any, associated with its use. It is the
partially substituted by Li, Pb, Zn, Be, Ba, or Ni.Amphiboles
are characterized by a complex monoclinic or orthorhombic
structure that includes a double chain of T-O tetrahedra with a
1
This test method is under the jurisdiction of ASTM Committee D22 on
Sampling andAnalysis ofAtmospheres and is the direct responsibility of Subcom-
3
mittee D22.07 on Asbestos. For referenced ASTM standards, visit the ASTM website, www.astm.org, or
Current edition approved April 1, 2004. Published May 2004. Originally contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
approved in 1998. Last previous edition approved in 1998 as D6281-98. Standards volume information, refer to the standard’s Document Summary page on
2
This test method was adapted from International Standard ISO10312 “Air the ASTM website.
4
quality - Determination of asbestos fibres - Direct transfer transmission electron Available fromAmerican National Standards Institute (ANSI), 25 W. 43rd St.,
microscopy method.” 4th Floor, New York, NY 10036.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1

---------------------- Page: 1 ----------------------
NOTICE: This standard has either been superseded and replaced by a new version or withdrawn. Contact ASTM
International (www.astm.org) for the latest informat
...

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Standard Test Method for Determination of Non-methane Organic Compounds (NMOC) in Ambient Air Using Cryogenic Preconcentration and Direct Flame Ionization Detection

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5.1 Many regulators, industrial processes, and other stakeholders require determination of NMOC in atmospheres.  
5.2 Accurate measurements of ambient NMOC concentrations are critical in devising air pollution control strategies and in assessing control effectiveness because NMOCs are primary precursors of atmospheric ozone and other oxidants (7, 8).  
5.2.1 The NMOC concentrations typically found at urban sites may range up to 1 ppm C to 3 ppm C or higher. In order to determine transport of precursors into an area monitoring site, measurement of NMOC upwind of the site may be necessary. Rural NMOC concentrations originating from areas free from NMOC sources are likely to be less than a few tenths of 1 ppm C.  
5.3 Conventional test methods based upon gas chromatography and qualitative and quantitative species evaluation are relatively time consuming, sometimes difficult and expensive in staff time and resources, and are not needed when only a measurement of NMOC is desired. The test method described requires only a simple, cryogenic pre-concentration procedure followed by direct detection with an FID. This test method provides a sensitive and accurate measurement of ambient total NMOC concentrations where speciated data are not required. Typical uses of this standard test method are as follows.  
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5.6.3 Ability to ship and store samples, if necessary,  
5.6.4 Unattended sample collection,  
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5.6.6 Collection of replicate samples for ...
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1.1 This test method2 presents a procedure for sampling and determination of non-methane organic compounds (NMOC) in ambient, indoor, or workplace atmospheres.  
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1.2.1 This test method describes a procedure for sampling in canisters at final pressures above atmospheric pressure (pressurized sampling).  
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Standard Guide for Selecting Volatile Organic Compounds (VOCs) and Semi-Volatile Organic Compounds (SVOCs) Emission Testing Methods to Determine Emission Parameters for Modeling of Indoor Environments

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4.1 Emissions of VOCs are typically controlled by internal mass-transfer limitations (for example, diffusion through the material), while emissions of SVOCs are typically controlled by external mass-transfer limitations (migration through the air immediately above the material). The emission of some chemicals may be controlled by both internal and external mass-transfer limitations. In addition, due to their lower vapor pressure, SVOCs generally adsorb to different media (chamber walls, building materials, particles, and other surfaces) at greater rates than VOCs. This sorption can increase the amount of time required to reach steady-state SVOC concentrations using conventional VOC emission test methods to months for a single test (2).  
4.2 Thus, existing methods for characterizing emissions of VOCs may not be appropriate or practical to properly characterize emission rates of SVOCs for use in modeling SVOC concentrations in indoor environments. A mass-transfer framework is needed to accurately assess emission rates of SVOCs when predicting the SVOC indoor air concentrations in indoor environments. The SVOC mass-transfer framework includes SVOC emission characteristics and its partition to multimedia including sorption to indoor surfaces, airborne particles, and settled dust. Once the SVOC emission parameters and partitioning coefficients have been determined, these values can be used to modeling SVOC indoor concentrations.
SCOPE
1.1 This guide is intended to serve as a foundation for understanding when to use emission testing methods designed for volatile organic compounds (VOCs) to determine area-specific emission rates that are typically used in modeling indoor air VOC concentrations and when to use emission testing methods designed for semi-volatile organic compounds (SVOCs) to determine mass transfer emission parameters that are typically used to model indoor air, dust, and surface SVOC concentrations.  
1.2 This guide discusses how organic chemicals are conventionally categorized with respect to volatility.  
1.3 This guide presents a simplified mass-transfer model describing organic chemical emissions from a material to bulk air. The values of the model parameters are shown to be specific to material/chemical/chamber combinations.  
1.4 This guide shows how to use a mass-transfer model to estimate whether diffusion of the chemical within the material or convective mass transfer of the chemical from the surface of the material to the overlying air limits chemical emissions from the material surface.  
1.5 This guide describes the range of different chambers that are available for emission testing. The chambers are classified as either dynamic or static and either conventional or sandwich. The chambers are categorized as being optimal to determine either the area-specific emission rate or mass-transfer emission parameters.  
1.6 This guide discusses the roles sorption and convective mass-transfer coefficients play in selecting the appropriate emission chamber and analysis method to accurately and efficiently characterize emissions from indoor materials for use in modeling indoor chemical concentrations.  
1.7 This guide recommends when to choose an emission test method that is optimized to determine either the area-specific emission rate or mass-transfer emission parameters. For chemicals where the controlling mass-transfer process is unknown, the guide outlines a procedure to determine if the chemical emission is controlled by convective mass transfer of the chemical from the material.  
1.8 This guide does not provide specific guidance for measuring emission parameters or conducting indoor exposure modeling.  
1.9 Mechanisms controlling emissions from wet and dry materials and products are different. This guide considers the emission of chemicals from dry materials and products. Examples of functional uses of VOCs and SVOCs that this guide applies to include blowing agents, ...

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ASTM
ASTM D8445-22a(Practice)
Standard Practice for Measuring Chemical Emissions from Spray Polyurethane Foam (SPF) Insulation Samples in a Large-scale Ventilated Enclosure

SIGNIFICANCE AND USE
5.1 The demand for SPF insulation in homes and commercial buildings has increased as emphasis on energy efficiency increases. In an effort to protect the health and safety of both trade workers and building occupants due to the application of SPF, it is essential that reentry/reoccupancy-times into the structure where SPF has been applied, be established.  
5.2 Concentrations of chemical emissions determined in large-scale ventilated enclosure studies conducted by this practice may be used to generate source emission terms for IAQ models.  
5.3 The emission factors determined using this practice may be used to evaluate comparability and scalability of emission factors determined in other environments.  
5.4 This practice was designed to determine emission factors for chemicals emitted by SPF insulation in a controlled room environment.  
5.5 New or existing formulations may be sprayed, and emissions may be evaluated by this practice. The user of this practice is responsible for ensuring analytical methods are appropriate for novel compounds present in new formulations (see Appendix X1 for target compounds and generic formulations).  
5.6 This practice may be useful for testing variations in emissions from non-ideal applications. Examples of non-ideal applications include those that are off-ratio, applied outside of recommended range of temperature and relative humidity, or applied outside of manufacturer recommendations for thickness.  
5.7 The determined emission factors are not directly applicable to all potential real-world applications of SPF. While this data can be used for VOCs to estimate indoor environmental concentrations beyond three days, the uncertainty in the predicted concentrations increases with increasing time. Estimating longer term chemical concentrations (beyond three days) for SVOCs is not recommended unless additional data (beyond this practice) is used, see (1).4  
5.8 During the application of SPF, chemicals deposited on the non-applie...
SCOPE
1.1 This practice describes procedures for measuring the chemical emissions of volatile and semi-volatile organic compounds (VOCs and SVOCs) from spray polyurethane foam (SPF) insulation samples in a large-scale ventilated enclosure.  
1.2 This practice is used to identify emission rates and factors during SPF application and up to three days following application.  
1.3 This practice can be used to generate emissions data for research activities or modeled for the purpose to inform potential reentry and reoccupancy times. Potential reentry and re-occupancy times only apply to the applications that meet manufacturer guidelines and are specific to the tested formulation.  
1.4 This practice describes emission testing at ambient room and substrate temperature and relative humidity conditions recognizing chemical emissions may differ at different room and substrate temperatures and relative humidity.  
1.5 This practice does not address all SPF chemical emissions. This practice addresses specific chemical compounds of potential health and regulatory concern including methylene diphenyl diisocyanate (MDI), polymeric MDI (MDI oligomeric polyisocyanates mixture), flame retardants, aldehydes, and VOCs including blowing agents, and catalysts. Although specific chemicals are discussed in this practice, other chemical compounds of interest can be quantified (see target compound and generic formulation list in Appendix X1). Other chemical compounds used in SPF such as polyols, emulsifiers, and surfactants are not addressed by this practice. Particulate sizing and distribution are also outside the scope of this practice.  
1.6 Emission rates during application are determined from air phase concentration measurements that may include particle bound chemicals. SVOC deposition to floors and ceilings is also quantified for post application modeling inputs. SVOC emission rates should only be used for modeling purposes for the durati...

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ASTM
ASTM D5110-22a(Practice)
Standard Practice for Calibration of Ozone Monitors and Certification of Ozone Transfer Standards Using Ultraviolet Photometry

SIGNIFICANCE AND USE
5.1 The reactivity and instability of O3 preclude the storage of O3 concentration standards for any practical length of time, and precludes direct certification of O3 concentrations as Standard Reference Materials (SRMs). Moreover, there is no available SRM that can be readily and directly adapted to the generation of O3 standards analogous to permeation devices and standard gas cylinders for sulfur dioxide and nitrogen oxides. Dynamic generation of O3 concentrations is relatively easy with a source of ultraviolet (UV) radiation. However, accurately certifying an O3 concentration as a primary standard requires assay of the concentration by a comprehensively specified analytical procedure, which must be performed every time a standard is needed (10).  
5.2 This practice is not designed for the routine calibration of O3 monitors at remote locations (see Practices D5011).
SCOPE
1.1 This practice covers a means for calibrating ambient, workplace, or indoor ozone monitors, and for certifying transfer standards to be used for that purpose.  
1.2 This practice describes means by which dynamic streams of ozone in air can be designated as primary ozone standards.  
1.3 The values stated in SI units are to be regarded as 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. See Section 8 for specific precautionary statements.  
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 D8407-21(Guide)
Standard Guide for Measurement Techniques for Formaldehyde in Air

SIGNIFICANCE AND USE
5.1 The objective of this guide is to provide the user with an information base on commercially available instruments and technologies that can be used to measure indoor air formaldehyde concentrations.  
5.2 This guide is intended as a repository for formaldehyde measurement technologies that other approved ASTM methods can reference to meet ASTM indoor air formaldehyde quantification needs.  
5.3 This guide does not discuss the equivalency of the technologies presented. Each technology may have positive or negative interferences that are unique to that technology. When using a new method, equivalence with old methods should be demonstrated for each matrix, measuring environment and media (that is, each type of wood for formaldehyde emission testing in chamber environments). This is especially true when the method is intended to generate regulatory compliance data. Demonstrating equivalence or compliance, or both, is beyond the scope of this method. For guidance equivalence see references such as 40 CFR § 136.6 and CEN Guide to the Demonstration of Equivalence of Ambient Air Monitoring Methods (1).5
SCOPE
1.1 This guide describes analytical methods for determining formaldehyde concentrations in air.  
1.2 The guide is primarily focused on formaldehyde measurement technologies applicable to indoor (including in vehicle and workplace) air and associated environments (that is, chambers or bags, or both, used for formaldehyde emission testing). The described technologies may be applicable to other environments (ambient outdoor).  
1.3 This guide reviews a range of commercially available technologies that can be used to measure indoor air formaldehyde concentrations. These technologies typically can measure airborne formaldehyde concentrations with detection limits in the range of 0.04 ppbv (0.05 µg m-3) to 10 ppbv (12 µg m-3). The described technologies are typically applied to research or regulatory applications and not consumer level uses.  
1.4 This guide describes the principles behind each method and their advantages and limitations.  
1.5 This guide does not attempt to differentiate between the effectiveness of the methods nor determine equivalence of the methods.  
1.6 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.  
1.7 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.  
1.8 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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