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<article xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:mml="http://www.w3.org/1998/Math/MathML" article-type="research-article"><?properties manuscript?><front><journal-meta><journal-id journal-id-type="nlm-journal-id">101189458</journal-id><journal-id journal-id-type="pubmed-jr-id">31897</journal-id><journal-id journal-id-type="nlm-ta">J Occup Environ Hyg</journal-id><journal-id journal-id-type="iso-abbrev">J Occup Environ Hyg</journal-id><journal-title-group><journal-title>Journal of occupational and environmental hygiene</journal-title></journal-title-group><issn pub-type="ppub">1545-9624</issn><issn pub-type="epub">1545-9632</issn></journal-meta><article-meta><article-id pub-id-type="pmid">25625781</article-id><article-id pub-id-type="pmc">4589148</article-id><article-id pub-id-type="doi">10.1080/15459624.2014.995302</article-id><article-id pub-id-type="manuscript">HHSPA723710</article-id><article-categories><subj-group subj-group-type="heading"><subject>Article</subject></subj-group></article-categories><title-group><article-title>Harmonization of NIOSH Sampling and Analytical Methods with Related International Voluntary Consensus Standards</article-title></title-group><contrib-group><contrib contrib-type="author"><name><surname>Ashley</surname><given-names>Kevin</given-names></name><role>Reported by</role></contrib><aff id="A1">US Department of Health and Human Services, Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health, 1090 Tusculum Avenue, Mail Stop R-7, Cincinnati, Ohio 45226-1998; <email>KAshley@cdc.gov</email></aff></contrib-group><contrib-group><contrib contrib-type="editor"><name><surname>Harper</surname><given-names>Martin</given-names></name><role>Column Editor</role></contrib></contrib-group><pub-date pub-type="nihms-submitted"><day>18</day><month>9</month><year>2015</year></pub-date><pub-date pub-type="ppub"><year>2015</year></pub-date><pub-date pub-type="pmc-release"><day>01</day><month>1</month><year>2016</year></pub-date><volume>12</volume><issue>7</issue><fpage>D107</fpage><lpage>D115</lpage><!--elocation-id from pubmed: 10.1080/15459624.2014.995302--></article-meta></front><body><sec sec-type="intro" id="S1"><title>INTRODUCTION</title><p id="P1">The <italic>NIOSH Manual of Analytical Methods</italic> (NMAM<sup>&#x000ae;</sup>) is a compilation of analytical methods for air, biological, surface (including dermal) and bulk samples, as well as biological specimens, that have been evaluated and validated in consideration of their fitness for purpose for workplace exposure monitoring. NIOSH sampling and analytical methods are intended to promote accuracy, sensitivity, and specificity in industrial hygiene analyses and related applications. NMAM is published online and is available worldwide free of charge.<sup><xref rid="R1" ref-type="bibr">1</xref></sup> Presently in its 5<sup>th</sup> edition, NMAM is constantly updated as new methods are developed and validated and as revised methods are re-evaluated and their performance verified. Often there are situations during use where certain NIOSH methods may require modification, for example, to accommodate interfering compounds from a particular workplace, to take advantage of unique laboratory capabilities, to make use of equivalent sample preparation or analysis techniques, or to make possible the analysis of a single sample for multiple contaminants. NIOSH methods are evaluated with respect to the NIOSH accuracy criterion <italic>A</italic> = &#x000b1;25%, wherein at least 95% of measurements must fall within 25% of the true (or reference) value.<sup><xref rid="R2" ref-type="bibr">2</xref></sup> When method modifications are made, quality control data demonstrating the reliability of the modified method must be obtained, recorded and reported. The methods published in NMAM are relied upon by authoritative bodies such as accrediting organizations and regulatory agencies. Besides sampling and analytical methods, NMAM also includes chapters on quality assurance, portable instrumentation, analysis of fibers, aerosol sampler design, and other guidance on specific areas of interest.</p><p id="P2">To address requirements for harmonized methods for use by occupational hygiene laboratories, international voluntary consensus standard test methods have been developed and promulgated by ASTM International,<sup><xref rid="R3" ref-type="bibr">3</xref></sup> the Comit&#x000e9; Europ&#x000e9;en de Normalisation<sup><xref rid="R4" ref-type="bibr">4</xref></sup> (European Committee for Standardization, CEN) and the International Organization for Standardization<sup><xref rid="R5" ref-type="bibr">5</xref></sup> (ISO). Like NIOSH methods, these consensus standard procedures describe aspects of sampling and sample preparation as well as measurement, although normally in exhaustive, specific detail. Other related consensus standards offer thorough guidance on sample collection, sample preparation and analytical protocols. Harmonization of NIOSH methods with related voluntary consensus standards is a strategic goal for the 5<sup>th</sup> edition of NMAM.</p><p id="P3">Current efforts to update NMAM may also include validated methodologies developed by sister organizations both nationally and internationally, such as the US Occupational Safety and Health Administration (OSHA), the Health and Safety Laboratory (HSL) in the United Kingdom, the Institut National de Recherche et de Securit&#x000e9; (National Institute of Research on Health and Safety at Work, INRS) in France and the the Institut f&#x000fc;r Arbeitsschutz der Deutschen Geseltzlichen Unfallversicherung (Institute for Occupational Safety and Health of the German Social Accident Insurances, IFA) in Germany. NIOSH is keeping abreast of new industrial hygiene and biomonitoring methods and consensus standards developed globally. NIOSH researchers coordinate and collaborate externally and often consider suitable validated methods developed by other institutes and organizations, domestic as well as international.</p></sec><sec id="S2"><title>HARMONIZATION OF ANALYTICAL METHODS</title><p id="P4">In accordance with and observance of the National Technology Transfer and Advancement Act (NTTAA),<sup><xref rid="R6" ref-type="bibr">6</xref></sup> a main goal of ongoing NIOSH methods development activities is to ensure that NIOSH methods are harmonized with relevant international voluntary consensus standards. The NTTAA directs US federal government agencies to: (1) rely on applicable voluntary consensus standards in lieu of procedures and documents developed in-house; and (2) participate in the development of pertinent consensus standards that are related to the agencies&#x02019; activities. In the course of sampling and analytical methods development, NIOSH may consider adapting applicable existing standards promulgated by ISO, CEN and/or ASTM International.</p><p id="P5">Regarding method evaluation and validation, an important standard published by CEN, i.e., EN 482, outlines the general requirements for measurement of chemical agents in workplace air.<sup><xref rid="R7" ref-type="bibr">7</xref></sup> This European standard specifies an upper limit for expanded uncertainty <italic>U</italic> of &#x000b1;30% for an acceptable sampling and analytical method when applied to measurements spanning the OEL (i.e., between 0.5 &#x02013; 2&#x000d7; the OEL). EN 482 also cites an upper limit for <italic>U</italic> of &#x000b1;50% for measurement of analyte levels between the method quantitation limit and &#x000bd; of the applicable OEL. It is pointed out that for most applications, expanded uncertainty (for coverage factor <italic>k</italic> of 2-3) is equivalent to accuracy as defined by NIOSH.<sup><xref rid="R8" ref-type="bibr">8</xref>,<xref rid="R9" ref-type="bibr">9</xref></sup> NIOSH<sup><xref rid="R2" ref-type="bibr">2</xref></sup> and CEN<sup><xref rid="R7" ref-type="bibr">7</xref></sup> method evaluation protocols account for all potential sources of experimental error (both random and systematic), in accordance with the ISO guidelines on measurement uncertainty.<sup><xref rid="R10" ref-type="bibr">10</xref></sup> For a given measurement method, the final estimate of accuracy or expanded uncertainty is a result of combined contributions from propagated errors occurring throughout the sampling and analytical process.</p><p id="P6">Of the more than 300 published NIOSH sampling and analytical methods,<sup><xref rid="R1" ref-type="bibr">1</xref></sup> a large number have related or parallel international voluntary consensus standards that have been produced by ASTM International,<sup><xref rid="R3" ref-type="bibr">3</xref></sup> ISO<sup><xref rid="R4" ref-type="bibr">4</xref></sup> and/or CEN<sup><xref rid="R5" ref-type="bibr">5</xref></sup> (<xref ref-type="table" rid="T1">Table I</xref>). In many instances the consensus standard procedures listed were developed with a basis on NIOSH methods, while in some cases NIOSH methods are themselves based on more recently developed ASTM and/or ISO standards. Ideally sampling and analytical methods for toxic agents in workplaces are performance-based, and harmonizing NIOSH methods with consensus standards is not necessarily as important as ensuring that the methods are adequately validated, sufficiently accurate and fit for purpose. NIOSH scientists have participated in the development of related consensus standards for many years. This helps to ensure that NIOSH methods are harmonized with applicable consensus standards and also fosters cooperation and collaboration between NIOSH experts and fellow scientists from domestic organizations and sister institutes in countries around the world.</p><p id="P7">As a related resource, the IFA in Germany, in cooperation with experts from other member European nations participating in deliberations of CEN Technical Committee (TC) 137,<sup><xref rid="R5" ref-type="bibr">5</xref></sup> has made available a database of over 225 validated sampling and analytical methods for more than 125 substances.<sup><xref rid="R11" ref-type="bibr">11</xref></sup> Ratings of methods for these analytes are provided based on factors established by a European expert committee.<sup><xref rid="R12" ref-type="bibr">12</xref></sup> Presently within CEN there is an ongoing project to update and expand this very useful methods database. Many NIOSH methods and international consensus standards can be found cited in this database.</p><p id="P8">Various older NIOSH methods for organics listed in <xref ref-type="table" rid="T1">Table I</xref>, such as those for organic gases and vapors, are based on the use of packed gas chromatography (GC) columns. In practice, packed GC columns are rarely used now and have been largely replaced by capillary GC columns. The use of capillary GC columns has been described in many of the more recently published consensus standards (ASTM International and ISO) listed in <xref ref-type="table" rid="T1">Table I</xref>. In order to modernize many of these older NIOSH methods (which were developed mostly in the 1970s and 1980s), there is a concerted effort to update a number of the NIOSH GC analytical methodologies for organic vapors and gases. Thus a project is now underway to validate a multi-analyte procedure (or procedures) that can be used to measure multiple gaseous organic compounds in occupational atmospheres by means of sorbent sampling and capillary GC separation / isolation, followed by appropriate detection schemes like flame ionization detection (FID), photoionization detection (PID) or mass spectrometry (MS). This will result in the promulgation of new NIOSH methods for toxic organic gases and vapors that are up to date and better harmonized with applicable international consensus standards.</p></sec><sec id="S3"><title>GUIDANCE DOCUMENTS</title><p id="P9">Within NMAM, separate from the sampling and analytical methods, are eighteen chapters covering a variety of subjects.<sup><xref rid="R1" ref-type="bibr">1</xref></sup> Explanatory chapters on quality assurance, sampling guidance, portable instrumentation, method development and evaluation, aerosol collection, measurement of specific analytes or groups of analytes, etc., provide valuable guidance to the users of NIOSH methods. These chapters provide a convenient resource that augments related consensus standards and technical information often available elsewhere in monographs and texts. Presently, efforts are underway to update several chapters that have not been revised in a number of years. Also, new chapters on key subjects including guidelines for the performance of biomonitoring methods and direct-reading instruments are planned. Similarly for sampling and analytical methods, harmonization of the guidelines put down in these chapters with relevant consensus standards guidance is essential and will be ensured.</p><p id="P10">Many of the methods published in NMAM specify the collection of workplace aerosol samples using filter samplers such as 37-mm closed-face filter cassettes (CFCs). NIOSH considers that all particles entering the sampler (e.g., CFC) should be included as part of the sample whether they deposit on the filter or on the inside surfaces of the sampler.<sup><xref rid="R13" ref-type="bibr">13</xref></sup> All aerosol particles entering occupational air samplers should be included in the sample for gravimetric analysis as well as for analytes such as metals and metalloids. Hence, during sample preparation and analysis, procedures should be used to account for material adhering to the internal walls of sampling cassettes. In the spirit of harmonization, consideration of internal sampler wall deposits is included in related international voluntary consensus standards that describe the sampling and analysis of airborne metals and metalloids.<sup><xref rid="R14" ref-type="bibr">14</xref>,<xref rid="R15" ref-type="bibr">15</xref></sup></p><p id="P11">Also linked to guidance on NMAM sampling and analytical procedures for gases and vapors are relevant ASTM International and ISO standards describing the evaluation of diffusive samplers.<sup><xref rid="R16" ref-type="bibr">16</xref>,<xref rid="R17" ref-type="bibr">17</xref></sup> Although validation of passive monitors<sup><xref rid="R18" ref-type="bibr">18</xref></sup> may be expensive (sometimes prohibitively so), the ability to obtain good estimates of analytical uncertainty for diffusive sampling techniques is important for achieving more accurate real-time exposure assessments. This is especially true of screening techniques, which typically require vast amounts of performance data to enable adequate characterization of overall measurement uncertainty (and consequent evaluation of fitness-for-purpose).<sup><xref rid="R19" ref-type="bibr">19</xref></sup> Harmonized guidance on diffusive sampling<sup><xref rid="R16" ref-type="bibr">16</xref>,<xref rid="R17" ref-type="bibr">17</xref></sup> should prove beneficial for evaluating newer passive monitoring techniques such as canister sampling, helium-diffusive sampling and solid-phase micro-extraction.</p><p id="P12">Increased use of direct-reading monitors for occupational hygiene applications<sup><xref rid="R20" ref-type="bibr">20</xref></sup> underscores the need for standardized evaluation and validation protocols for these devices. Recently, guidance on evaluation of direct-reading instruments for gas and vapor monitoring has become available from NIOSH,<sup><xref rid="R21" ref-type="bibr">21</xref></sup> for example with applications to four-gas monitors. Currently there are efforts to develop international voluntary consensus standards for real-time monitoring devices that will accommodate not only onsite quantitative analysis but also screening techniques for myriad applications.</p></sec><sec id="S4"><title>CONCLUDING REMARKS</title><p id="P13">Further efforts are currently underway that will fulfill requirements for fully validated NIOSH and consensus standard procedures for workplace exposure measurements. For example, new procedures describing the analysis of all aerosol particles entering a given air sampling device are being developed and evaluated. Through effective use of national and international collaborations and resources, further advances in the field of industrial hygiene chemistry are underway and improvements in sampling and analytical protocols are continually being explored. The <italic>NIOSH Manual of Analytical Methods</italic> remains an invaluable global resource for the occupational hygiene profession. Harmonization with voluntary consensus standards organizations such as ASTM International, CEN and ISO is crucial in leveraging current and future applied research, as well as technology transfer endeavors, within the discipline of occupational hygiene sampling and analysis.</p></sec></body><back><ack id="S5"><title>Acknowledgments</title><p>Thanks to Rosa Key-Schwartz, Alan Echt, Brian Curwin and Gayle DeBord for review of the draft manuscript.</p><p>This article was prepared by US government employees as part of their official duties and legally may not be copyrighted in the United States of America. Mention of any company or product does not constitute endorsement by the National Institute for Occupational Safety and Health (NIOSH). In addition, citations to Web sites external to NIOSH do not constitute NIOSH endorsement of the sponsoring organizations or their programs or products. Furthermore, NIOSH is not responsible for the content of these Web sites. All Web addresses referenced in this document were accessible as of the publication date. 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No. 2012-162</comment><comment><ext-link ext-link-type="uri" xlink:href="http://www.cdc.gov/niosh/docs/2012-162">www.cdc.gov/niosh/docs/2012-162</ext-link></comment></element-citation></ref></ref-list></back><floats-group><table-wrap id="T1" position="float" orientation="portrait"><label>TABLE I</label><caption><title>NIOSH Sampling and Analytical Methods and Related / Parallel International Voluntary Consensus Standards</title></caption><table frame="box" rules="all"><thead><tr><th align="left" valign="top" rowspan="1" colspan="1">
<italic>NIOSH Method(s)</italic>
<sup><xref rid="R1" ref-type="bibr">1</xref></sup>
</th><th align="left" valign="top" rowspan="1" colspan="1">
<italic>ASTM Standard(s)</italic>
<sup><xref rid="R3" ref-type="bibr">3</xref></sup>
</th><th align="left" valign="top" rowspan="1" colspan="1">
<italic>ISO Standard(S)</italic>
<sup><xref rid="R4" ref-type="bibr">4</xref></sup>
</th><th align="left" valign="top" rowspan="1" colspan="1">
<italic>CEN (EN) Standard(s)</italic>
<sup><xref rid="R5" ref-type="bibr">5</xref></sup>
</th></tr></thead><tbody><tr><td align="left" valign="top" rowspan="1" colspan="1">0500 &#x00026; 0501, Particles<break/>not otherwise regulated,<break/>total (gravimetric)<break/>5000 &#x00026; 5100, Carbon<break/>black (gravimetric)</td><td align="left" valign="top" rowspan="1" colspan="1">D6552, Controlling and<break/>characterizing errors in<break/>weighing collected<break/>aerosols</td><td align="left" valign="top" rowspan="1" colspan="1">15767, Controlling<break/>and characterizing<break/>uncertainty in<break/>weighing collected<break/>aerosols</td><td align="left" valign="top" rowspan="1" colspan="1">
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</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">0600, Particles not<break/>otherwise regulated,<break/>respirable (gravimetric)</td><td align="left" valign="top" rowspan="1" colspan="1">D4532, Respirable dust<break/>in workplace<break/>atmospheres<break/>D6552, Controlling<break/>errors in weighing<break/>collected aerosols</td><td align="left" valign="top" rowspan="1" colspan="1">15767, Controlling<break/>and characterizing<break/>uncertainty in<break/>weighing collected<break/>aerosols</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">0800, Bioaerosols (by<break/>pumped sampling)<break/>0900, Mycobacterium<break/>tuberculosis (filter<break/>sampling)</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">13137, Pumps for<break/>sampling chemical &#x00026;<break/>biological agents</td><td align="left" valign="top" rowspan="1" colspan="1">13098, Guidelines for<break/>measuring microorganisms<break/>&#x00026; endotoxin<break/>13137, Pumps for<break/>sampling chemical &#x00026;<break/>biological agents<break/>14583, Bioaerosol<break/>sampling &#x02013; requirements<break/>&#x00026; methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">1003, Halogenated<break/>hydrocarbons, by sorbent<break/>tube &#x00026; gas chromatography (GC)<break/>1022, Trichloroethylene<break/>by sorbent tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D3686, Sampling<break/>organic vapors by<break/>charcoal tube<break/>D3687, Analysis of<break/>organic vapors<break/>collected by charcoal<break/>tube</td><td align="left" valign="top" rowspan="1" colspan="1">9486, Vaporous<break/>chlorinated<break/>hydrocarbons by<break/>charcoal tube / solvent<break/>desorption / GC</td><td align="left" valign="top" rowspan="1" colspan="1">1076, Gases and vapor<break/>measurement by pumped<break/>sampling &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">1007, Vinyl chloride by<break/>charcoal tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D4766, Vinyl chloride<break/>by charcoal tube</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">1008-1460, Organic<break/>vapors (various) by<break/>charcoal tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D3686, Sampling<break/>organic vapors by<break/>charcoal tube<break/>D3687, Analysis of<break/>organic vapors<break/>collected by charcoal<break/>tube</td><td align="left" valign="top" rowspan="1" colspan="1">16017-1, Organic<break/>vapors by charcoal<break/>tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">1076, Gases and vapor<break/>measurement by pumped<break/>sampling &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">1500, Hydrocarbons, BP<break/>36-126 &#x000b0;C, by charcoal<break/>tube &#x00026; GC<break/>1501, Aromatic<break/>hydrocarbons by charcoal<break/>tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D3686, Sampling<break/>organic vapors by<break/>charcoal tube<break/>D3687, Analysis of<break/>organic vapors<break/>collected by charcoal tube</td><td align="left" valign="top" rowspan="1" colspan="1">16017-1, Organic<break/>vapors by charcoal<break/>tube &#x00026; GC<break/>9487, Vaporous<break/>aromatic hydrocarbons<break/>by charcoal tube / solvent desorption / GC</td><td align="left" valign="top" rowspan="1" colspan="1">1076, Gases and vapor<break/>measurement by pumped<break/>sampling &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">1614, Ethylene oxide by<break/>charcoal tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D4413, Ethylene oxide,<break/>charcoal tube sampling<break/>D5578, Ethylene oxide,<break/>derivatization technique</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">2001, Aromatic amines<break/>by sorbent tube &#x00026; GC<break/>2010, Aliphatic amines<break/>by sorbent tube &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D3686, Sampling<break/>organic vapors by<break/>charcoal tube<break/>D3687, Analysis of<break/>organic vapors<break/>collected by charcoal<break/>tube</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">2018, Aliphatic aldehydes<break/>by derivatized silica<break/>cartridge &#x00026; liquid<break/>chromatography (LC)<break/>2539, Aldehydes,<break/>screening, by GC / GC<break/>GC-mass spectrometry<break/>(MS)</td><td align="left" valign="top" rowspan="1" colspan="1">D5197, Formaldehyde<break/>and other carbonyls by<break/>derivatized silica<break/>cartridge &#x00026; LC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1"/></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">2549, Volatile organic<break/>compounds (VOCs) by<break/>sorbent tube / thermal<break/>desorption / GC-MS</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">16200-1, VOCs by<break/>solvent desorption /<break/>GC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">3600 &#x00026; 3601, Maneb by<break/>dermal patch &#x00026; hand<break/>wash (respectively)</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">TR 14294,<break/>Measurement of<break/>dermal exposure</td><td align="left" valign="top" rowspan="1" colspan="1">TS 15278, Evaluation<break/>strategy for dermal<break/>exposure TR 15279, Measurement<break/>of dermal exposure</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">3700, Benzene by<break/>portable GC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">4554-1, -2, -3 &#x00026; -4, Direct<break/>measurement of toxic<break/>gases and vapours</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">3800, Inorganic and<break/>organic gases by<break/>extractive Fourier<break/>transform infrared (FTIR)<break/>spectrometry</td><td align="left" valign="top" rowspan="1" colspan="1">E1982, Gases and<break/>vapors by open-path<break/>FTIR spectrometry</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">4554-1, -2, -3 &#x00026; -4, Direct<break/>measurement of toxic<break/>gases and vapours</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5040, Elemental carbon<break/>(diesel particles) by<break/>thermo-optical analysis</td><td align="left" valign="top" rowspan="1" colspan="1">D6877, Diesel<break/>particulate exhaust by<break/>thermo-optical analysis</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">14530, Diesel particulate<break/>matter &#x02013; general<break/>requirements</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5042, Benzene-soluble<break/>particulate matter</td><td align="left" valign="top" rowspan="1" colspan="1">D4600, Benzene-<break/>soluble particulate<break/>matter D6494, Asphalt fume<break/>in benzene-soluble<break/>fraction</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5503, Polychlorobiphenyls by<break/>filter + sorbent &#x00026; GC</td><td align="left" valign="top" rowspan="1" colspan="1">D4861, Pesticides and<break/>polychlorinated<break/>biphenyls &#x02013; guidance<break/>on sampling and<break/>analytical methods</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5521, Monomeric<break/>isocyanates by impinger<break/>sampling &#x00026; LC 5522, Isocyanates by<break/>impinger sampling &#x00026; LC<break/>5525, Isocyanates, total,<break/>by filter or impinger<break/>sampling &#x00026; LC</td><td align="left" valign="top" rowspan="1" colspan="1">D5836 &#x00026; 5932,<break/>Toluene diisocyanates<break/>(TDI) by LC<break/>D6561, Hexamethylene<break/>diisocyanate (HDI)<break/>aerosol by LC<break/>D6562, Gaseous HDI<break/>by LC</td><td align="left" valign="top" rowspan="1" colspan="1">11734-1, Isocyanates<break/>by LC-MS; 11734-2,<break/>Amines &#x00026; aminoisocyanates by<break/>LC-MS<break/>11735, Total<break/>isocyanates by LC<break/>11736, Isocyanate by<break/>double-filter sampling<break/>&#x00026; LC<break/>16702, Total organic<break/>isocyanates by LC<break/>17737, Guidelines for<break/>selecting isocyanate<break/>methods</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5524, Metalworking<break/>fluids &#x02013; gravimetric<break/>analysis</td><td align="left" valign="top" rowspan="1" colspan="1">D7049, Metal removal<break/>fluid aerosol</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1"/></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5506, Polynuclear<break/>aromatic hydrocarbons by<break/>filter + sorbent &#x00026; LC<break/>5515, Polynuclear<break/>aromatic hydrocarbons by<break/>filter + sorbent &#x00026; GC<break/>5800 Polycyclic aromatic<break/>compounds by filter +<break/>sorbent &#x00026; flow-injection<break/>analysis</td><td align="left" valign="top" rowspan="1" colspan="1">D6209, Polycyclic<break/>aromatic compounds by<break/>sorbent-backed filter &#x00026;<break/>GC-MS</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">5600, Organophosphorus<break/>pesticides by filter +<break/>sorbent &#x00026; GC<break/>5601, Organonitrogen<break/>pesticides by filter +<break/>sorbent &#x00026; LC</td><td align="left" valign="top" rowspan="1" colspan="1">D4861, Pesticides and polychlorinated biphenyls</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">6004, SO<sub>2</sub> by treated<break/>filter &#x00026; IC</td><td align="left" valign="top" rowspan="1" colspan="1">D2914, SO<sub>2</sub> by bubbler<break/>&#x00026; colorimetry</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1"/></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">6009, Hg by sorbent tube<break/>&#x00026; cold vapor atomic<break/>absorption (CVAA)</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">17733, Hg by CVAA<break/>or cold vapor atomic<break/>fluorescence</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">6013, H<sub>2</sub>S by charcoal<break/>tube and ion<break/>chromatography (IC)</td><td align="left" valign="top" rowspan="1" colspan="1">4913, H<sub>2</sub>S by length of<break/>stain reading</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">6014, NO &#x00026; NO<sub>2</sub> by<break/>sorbent tube &#x00026; visible<break/>absorption<break/>spectrophotometry<break/>6700, NO<sub>2</sub> by diffusive<break/>sampler &#x00026; visible<break/>absorption<break/>spectrophotometry</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">8761, NO2 by detector<break/>tube &#x00026; direct<break/>indication</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">6604, CO by<break/>electrochemical sensor</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">8760, CO by detector<break/>tube</td><td align="left" valign="top" rowspan="1" colspan="1">4554-1, -2, -3 &#x00026; -4, Direct<break/>measurement of toxic<break/>gases and vapours</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7013, Al; 7020, Ca; 7024,<break/>Cr; 7027, Co; 7029, Cu;<break/>7030, Zn; 7048, Cd;<break/>7074, W (insoluble);<break/>7082, Pb, by flame<break/>atomic absorption<break/>spectrometry (FAAS)</td><td align="left" valign="top" rowspan="1" colspan="1">D4185, Metals by<break/>FAAS D6785, Pb by FAAS or<break/>graphite furnace atomic<break/>absorption spectrometry (GFAAS)</td><td align="left" valign="top" rowspan="1" colspan="1">8518, Pb by FAAS or<break/>electrothermal atomic<break/>absorption (ETAAS)<break/>11174, Cd by FAAS<break/>or ETAAS</td><td align="left" valign="top" rowspan="1" colspan="1">13890, Metals &#x00026;<break/>metalloids &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7056, Ba, soluble<break/>compounds; 7074, W<break/>(solubles), by FAAS</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">15202-2, Annex B:<break/>Soluble metals and<break/>metalloids in<break/>workplace air</td><td align="left" valign="top" rowspan="1" colspan="1">13890, Metals &#x00026;<break/>metalloids &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7105, Pb by GFAAS</td><td align="left" valign="top" rowspan="1" colspan="1">D6785, Pb by FAAS or<break/>GFAAS</td><td align="left" valign="top" rowspan="1" colspan="1">8518, Pb by FAAS or<break/>ETAAS</td><td align="left" valign="top" rowspan="1" colspan="1">13890, Metals &#x00026;<break/>metalloids &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7300, 7301, 7302, 7303,<break/>7304 Elements by ICP-<break/>AES</td><td align="left" valign="top" rowspan="1" colspan="1">D7035, Metals and<break/>metalloids by ICP-AES</td><td align="left" valign="top" rowspan="1" colspan="1">15202-1, -2 &#x00026; -3,<break/>Metals and metalloids<break/>by ICP-AES<break/>(sampling, preparation<break/>and analysis)</td><td align="left" valign="top" rowspan="1" colspan="1">13890, Metals &#x00026;<break/>metalloids &#x02013; requirements<break/>&#x00026; test methods</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7400, Asbestos fibers by<break/>phase-contrast<break/>microscopy (PCM)<break/>7402, Asbestos fibers by<break/>transmission electron<break/>microscopy (TEM)</td><td align="left" valign="top" rowspan="1" colspan="1">D7200, Airborne fibers<break/>in mines &#x00026; quarries,<break/>including asbestos, by<break/>PCM &#x00026; TEM<break/>D7201, Asbestos fibers<break/>by PCM with TEM<break/>option</td><td align="left" valign="top" rowspan="1" colspan="1">8672, Airborne<break/>inorganic fibres by<break/>PCM</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7401, Alkaline dusts, by<break/>acid-base titration</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">17091, LiOH, NaOH,<break/>KOH &#x00026; CaOH<sub>2</sub> by<break/>suppressed IC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7500, Respirable<break/>crystalline silica (RCS)<break/>by X-ray diffraction<break/>(XRD)<break/>7602, RCS by infrared<break/>(IR)<break/>7603, RCS in coal mine<break/>dust</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">24095, Guidance for<break/>measuring respirable<break/>crystalline silica</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7600 &#x00026; 7703, Cr(VI) by<break/>Ultraviolet-Visible (UV-<break/>Vis) spectrophotometry<break/>7605, Cr(VI) by IC and<break/>UV-Vis detection</td><td align="left" valign="top" rowspan="1" colspan="1">D6832, Cr(VI) by IC<break/>and UV-Vis detection</td><td align="left" valign="top" rowspan="1" colspan="1">16740, Cr(VI) by IC<break/>and UV-Vis detection</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7704, Be in air by<break/>fluorescence<break/>9110, Be in wipes by<break/>fluorescence</td><td align="left" valign="top" rowspan="1" colspan="1">D7202, Be in air or<break/>wipes by fluorescence<break/>D7296, Be in dry wipes<break/>D7707, Be wipe<break/>specification</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7910, Arsenic trioxide by<break/>GFAAS</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">11041, Arsenic and<break/>arsenic trioxide by<break/>atomic absorption</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7902, Fluorides, aerosol<break/>&#x00026; gas, by ion-selective<break/>electrode (ISE)</td><td align="left" valign="top" rowspan="1" colspan="1">D4765, Fluorides by<break/>ISE</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7906, Fluorides, aerosol<break/>&#x00026; gas, by IC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">21438-3, Fluorides,<break/>aerosol &#x00026; gas, by IC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7907, HCl, HBr &#x00026; HNO<sub>3</sub><break/>by IC</td><td align="left" valign="top" rowspan="1" colspan="1">D7773, HCl, HBr &#x00026;<break/>HNO<sub>3</sub> by suppressed IC</td><td align="left" valign="top" rowspan="1" colspan="1">21438-2, HCl, HBr &#x00026;<break/>HNO<sub>3</sub>, by IC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">7908, H<sub>2</sub>SO<sub>4</sub> &#x00026; H<sub>3</sub>PO<sub>4</sub> by<break/>IC</td><td align="left" valign="top" rowspan="1" colspan="1">D4856, H<sub>2</sub>SO<sub>4</sub> by IC</td><td align="left" valign="top" rowspan="1" colspan="1">21438-1, H<sub>2</sub>SO<sub>4</sub> &#x00026;<break/>H<sub>3</sub>PO<sub>4</sub> by IC</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">9100 &#x00026; 9105, Pb on<break/>wipes<break/>9102, Elements on wipes</td><td align="left" valign="top" rowspan="1" colspan="1">D6966, Wipe sampling<break/>for metals<break/>D7659, Guide for<break/>elemental surface<break/>sampling<break/>D7822, Dermal wipe<break/>sampling for elemental<break/>analysis<break/>E7192, Pb wipe<break/>specification</td><td align="left" valign="top" rowspan="1" colspan="1">TR 14294,<break/>Measurement of<break/>dermal exposure</td><td align="left" valign="top" rowspan="1" colspan="1">TS 15278, Evaluation<break/>strategy for dermal<break/>exposure<break/>TR 15279, Measurement<break/>of dermal exposure</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">9200 &#x00026; 9201,<break/>Chlorinated and<break/>organonitrogen<break/>herbicides, hand wash &#x00026;<break/>dermal patch<break/>(respectively)<break/>9202 &#x00026; 9205, Captan and<break/>thiophanate-methyl in<break/>hand rinse and dermal<break/>patch (respectively)</td><td align="left" valign="top" rowspan="1" colspan="1">
&#x02014;
</td><td align="left" valign="top" rowspan="1" colspan="1">TR 14294,<break/>Measurement of<break/>dermal exposure</td><td align="left" valign="top" rowspan="1" colspan="1">TS 15278, Evaluation<break/>strategy for dermal<break/>exposure<break/>TR 15279, Measurement<break/>of dermal exposure</td></tr></tbody></table></table-wrap></floats-group></article>