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ASTM F1011-22

(Guide)

Standard Guide for Developing a Hazardous Materials Training Curriculum for Initial Response Personnel

Standard Guide for Developing a Hazardous Materials Training Curriculum for Initial Response Personnel

SIGNIFICANCE AND USE
4.1 This guide summarizes the typical contents of a course to aid emergency response team training organizations in selecting important subjects for inclusion in existing or new training programs.
SCOPE
1.1 This guide covers a format for a hazardous materials spill initial response team training curriculum. This guide is designed to assist trainers of initial response personnel in assessing the content of training curriculum by providing guidelines for subject content against which these curricula may be evaluated. The guide should be tailored by the trainer to fit specific circumstances that are present in the community or industry where a spill may occur.  
1.2 Sections 5, 6, 7, 8, and 9 of this guide identify those training areas that should be considered in a curriculum. The area of preplanning is listed and this topic should be seriously considered by the user. Training is only a small part of an overall spill response contingency plan. A properly equipped and trained spill response team cannot operate without a previously agreed plan of attack.  
1.3 Currently the U.S. Code of Federal Regulation 29 CFR 1910.120, 40 CFR 112 Subpart B, 40 CFR 264 Subpart D, 40 CFR 265 Subpart D, and 49 CFR 172 Subpart H specify that producers, handlers, and shippers of hazardous materials shall plan and train for hazardous spill response. Additional training may be required for shipments by vessel (49 CFR 176.13) and highway (49 CFR 177.800). Regardless of the above regulatory requirements, training is essential to a proper response in an emergency.  
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.

General Information

Status
Published
Publication Date
31-Dec-2021
ICS
13.300 - Protection against dangerous goods
Technical Committee
F20 - Hazardous Substances and Oil Spill Response
Drafting Committee
F20.21 - Initial Response Actions
Current Stage
Ref Project

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Standards Content (Sample)

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.
Designation: F1011 − 22
Standard Guide for
Developing a Hazardous Materials Training Curriculum for
1
Initial Response Personnel
This standard is issued under the fixed designation F1011; 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 mendations issued by the World Trade Organization Technical
Barriers to Trade (TBT) Committee.
1.1 This guide covers a format for a hazardous materials
spill initial response team training curriculum. This guide is
2. Referenced Documents
designed to assist trainers of initial response personnel in
2
assessing the content of training curriculum by providing
2.1 Federal Regulations:
guidelines for subject content against which these curricula
29 CFR 1910.120 - Hazardous waste operations and emer-
may be evaluated. The guide should be tailored by the trainer
gency response (OSHA HAZWOPER)
to fit specific circumstances that are present in the community
40 CFR 112 —Oil Pollution Prevention, SubpartB-Re-
or industry where a spill may occur.
quirements for Petroleum Oils and Non-Petroleum Oils
49 CFR 172 —Hazardous Materials Table, Special
1.2 Sections 5, 6, 7, 8, and 9 of this guide identify those
Provisions, Hazardous Materials Communications, Emer-
training areas that should be considered in a curriculum. The
gency Response Information, Training Requirements, and
area of preplanning is listed and this topic should be seriously
Security Plans, Subpart H
considered by the user. Training is only a small part of an
49 CFR 176.13 Carriage by Vessel - Responsibility for
overall spill response contingency plan. A properly equipped
compliance and training
and trained spill response team cannot operate without a
49 CFR 177.800 Carriage by Public Highway – Purpose and
previously agreed plan of attack.
scope of this part and responsibility for compliance and
1.3 Currently the U.S. Code of Federal Regulation 29 CFR
training
1910.120, 40 CFR 112 Subpart B, 40 CFR 264 Subpart D, 40
40 CFR 264 , Subpart D – Standards for Owners and
CFR 265 Subpart D, and 49 CFR 172 Subpart H specify that
Operators of Hazardous Waste Treatment, Storage, and
producers, handlers, and shippers of hazardous materials shall
Disposal Facilities, Contingency Plan and Emergency
plan and train for hazardous spill response.Additional training
Procedures
may be required for shipments by vessel (49 CFR 176.13) and
40 CFR 265 , Subpart D - Interim Status Standards for
highway(49CFR177.800).Regardlessoftheaboveregulatory
Owners and Operators of Hazardous Waste Treatment,
requirements, training is essential to a proper response in an
Storage, and Disposal Facilities, Contingency Plan and
emergency.
Emergency Procedures.
1.4 This standard does not purport to address all of the
2.2 Other Documents:
safety concerns, if any, associated with its use. It is the 3
2020 Emergency Response Guide Book
responsibility of the user of this standard to establish appro-
NIOSH —Pocket Guide to Chemical Hazards, PDF (2005),
priate safety, health, and environmental practices and deter- 4
ISO/ZIP (2010)
5
mine the applicability of regulatory limitations prior to use.
Safety Data Sheets
1.5 This international standard was developed in accor-
dance with internationally recognized principles on standard-
ization established in the Decision on Principles for the
2
AvailablefromU.S.GovernmentPrintingOfficeSuperintendentofDocuments,
Development of International Standards, Guides and Recom-
732 N. Capitol St., NW, Mail Stop: SDE, Washington, DC 20401, https://
www.ecfr.gov
3
Available from Transport Canada’s Website (last revised 2020) https://
tc.canada.ca/en/dangerousgoods/canutec/2020-emergency-response-guidebook-pdf-
1
This guide is under the jurisdiction of ASTM Committee F20 on Hazardous version.
4
Substances and Oil Spill Responseand is the direct responsibility of Subcommittee Available from CDC (Centers for Disease Control and Prevention) website –
F20.21 on Initial Response Actions. The National Institute for Occupational Safety and Health as updated online guide,
Current edition approved Jan. 1, 2022. Published April 2022. Originally PDF, and iPhone or Android App. https://www.cdc.gov/niosh/npg/
5
approved in 1986. Last previous edition approved in 2013 as F1011 – 07(2013). Safety Data Sheets are available from the specific chemical manufacturers
DOI: 10.1520/F1011-22. and/or distributors.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocke
...

This document is not an ASTM standard and is intended only to provide the user of an ASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation: F1011 − 07 (Reapproved 2013) F1011 − 22
Standard Guide for
Developing a Hazardous Materials Training Curriculum for
1
Initial Response Personnel
This standard is issued under the fixed designation F1011; 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
1.1 This guide covers a format for a hazardous materials spill initial response team training curriculum. This guide is designed
to assist trainers of initial response personnel in assessing the content of training curriculum by providing guidelines for subject
content against which these curricula may be evaluated. The guide should be tailored by the trainer to fit specific circumstances
that are present in the community or industry where a spill may occur.
1.2 Sections 5, 6, 7, 8, and 9 of this guide identify those training areas that should be considered in a curriculum. The area of
preplanning is listed and this topic should be seriously considered by the user. Training is only a small part of an overall spill
response contingency plan. A properly equipped and trained spill response team cannot operate without a previously agreed plan
of attack.
1.3 Currently the U.S. Code of Federal Regulation 29 CFR 1910.120, 40 CFR 112, 40 CFR 265, 112 Subpart B, 40 CFR 264
Subpart D, 40 CFR 265 Subpart D, and 49 CFR 173 172 Subpart H specify that producers, handlers, and shippers of hazardous
materials shall plan and train for hazardous spill response. The broad interpretation of these regulations could include the
requirement to train state and local response organizations who Additional training may be required to handle hazardous materials
in an emergency spill situation. for shipments by vessel (49 CFR 176.13) and highway (49 CFR 177.800). Regardless of the above
regulatory requirements, training is essential to a proper response in an emergency.
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 safety, health, and healthenvironmental 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.
2. Referenced Documents
2
2.1 Federal Regulations:
29 CFR 1910.120 - Hazardous waste operations and emergency response (OSHA HAZWOPER)
40 CFR 112 CFR 112—Oil —Oil Pollution Prevention, Subpart
B - Requirements for Petroleum Oils and Non-Petroleum Oils
1
This guide is under the jurisdiction of ASTM Committee F20 on Hazardous Substances and Oil Spill Responseand is the direct responsibility of Subcommittee F20.21
on Initial Response Actions.
Current edition approved April 1, 2013Jan. 1, 2022. Published April 2013April 2022. Originally approved in 1986. Last previous edition approved in 20072013 as
F1011 – 07.F1011 – 07(2013). DOI: 10.1520/F1011-07R13.10.1520/F1011-22.
2
Available from U.S. Government Printing Office Superintendent of Documents, 732 N. Capitol St., NW, Mail Stop: SDE, Washington, DC 20401, http://
www.access.gpo.gov. https://www.ecfr.gov
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 ----------------------
F1011 − 22
49 CFR 172 —Hazardous Materials Table, Special Provisions, Hazardous Materials Communications, Emergency Response
Information, Training Requirements, and Security Plans, Subpart H
49 CFR 176.13 Carriage by Vessel - Responsibility for compliance and training
49 CFR 177.800 Carriage by Public Highway – Purpose and scope of this part and responsibility for compliance and training
40 CFR 264 , Subpart D – Standards for Owners and Operators of Hazardous Waste Treatment, Storage, and Disposal Facilities,
Contingency Plan and Emergency Procedures
40 CFR 265 CFR 265—Interim , Subpart D - Interim Status Standards for Owners and Operators of Hazardous Waste Treatment,
Storage, and Disposal Facilities, Contingency Plan and Emergency Procedures.
2
49 CFR 173—Shippers—General R
...

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4.1 In order to ensure data consistency, it is important to use standardized terminology and definitions in describing oiling conditions (1)3. This guide provides a template for that purpose.  
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3.1 Systematic surveys provide data on shoreline, lakeshore, river bank or other terrain’s character and oiling conditions from which informed planning and operational decisions can be developed with respect to cleanup (1-4).3 In particular, the data are used by decision makers to determine which oiled areas require treatment and to develop end-point criteria for use as targets for the field operations.  
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3.2.1 The aerial reconnaissance survey phase provides a perspective on the overall extent and general nature of the oiling conditions. This information is used in conjunction with environmental, resource, and cultural sensitivity data to guide shoreline protection, recovery of mobile oil, and to facilitate the more detailed response planning and priorities of the response operations.  
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3.2.4 The post-treatment inspection ground survey or monitoring phase provides the necessary information and data to ensure a segment, that is part of the response program, has been treated to the approved end-point criterion. (5)  
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1.3.1 For the purpose of this guide, marine and estuarine shorelines, river banks, and lake shores will be collectively referred to as shorelines, shores, or shore-zones.  
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1.4 Other non-shoreline, inland habitats include wetlands (pond, fen, bog, swamp, tundra, and shrub) and drier terrains (grassland, desert, forests), and will be collectively referred to as either wetlands or terrains, respectively.  
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5.1 The LFL and UFL of gases and vapors define the range of flammable concentrations in air.  
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Section  
Section  
Scope  
1  
Referenced Documents  
2  
Terminology  
3  
Definitions  
3.1  
Definitions of Terms Specific to This Standard  
3.2  
Symbols  
3.3  
Summary of Test Method  
4  
Significance and Use  
5  
Interferences  
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Apparatus  
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Sampling  
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Test Specimens  
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Specimen Preparation  
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Calibration  
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Intercept Lengths  
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Grain Counts  
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Grain Areas  
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ALA Grain Size  
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Two-Phase Grain Structures  
12.7  
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13.5  
Intersection Counts  
13.6  
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SCOPE
1.1 This test method covers a procedure for measuring the threshold-limit conditions to allow equilibrium of combustion of materials in various oxidant gases under specific test conditions of pressure, temperature, flow condition, fire-propagation directions, and various other geometrical features of common systems.  
1.2 This test method is patterned after Test Method D2863-95 and incorporates its procedure for measuring the limit as a function of oxidant concentration for the most commonly used test conditions. Sections 8, 9, 10, 11, 13, and  for the basic oxidant limit (oxygen index) procedure are quoted directly from Test Method D2863-95. Oxygen index data reported in accordance with Test Method D2863-95 are acceptable substitutes for data collected with this standard under similar conditions.  
1.3 This test method has been found applicable to testing and ranking various forms of materials. It has also found limited usefulness for surmising the prospect that materials will prove “oxygen compatible” in actual systems. However, its results do not necessarily apply to any condition that does not faithfully reproduce the conditions during test. The fire limit is a measurement of a behavioral property and not a physical property. Uses of these data are addressed in Guides G63 and G94.  
Note 1: Although this test method has been found applicable for testing a range of materials in a range of oxidants with a range of diluents, the accuracy has not been determined for many of these combinations and conditions of specimen geometry, outside those of the basic procedure as applied to plastics.
Note 2: Test Method D2863-95 has been revised and the revised Test Method has been issued as D2863-97. The major changes involve sample dimensions, burning criteria and the method for determining the oxygen index. The aim of the revisions was to align Test Method D2863 with ISO 4589-2. Six laboratories conducted comparison round robin testing on self-supporting plastics and cellular materials using D2863-95 and D2863-97. The results indicate that there is no difference between the means provided y the two methods at the 95 % confidence level. No comparison tests were conducted on thin films. The majority of ASTM Committee G4 favors maintaining the D2863-95 as the backbone of G125 until comprehensive comparison data become available.  
1.4 One very specific set of test conditions for measuring the fire limits of metals in oxygen has been codified in Test Method G124. Test Method G124 measures the minimum pressure limit in oxygen fo...

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ASTM E1191-03A(2023)e1(Guide)
Standard Guide for Conducting Life-Cycle Toxicity Tests with Saltwater Mysids

SIGNIFICANCE AND USE
5.1 Protection of a species requires prevention of unacceptable effects on the number, weight, health, and uses of the individuals of that species. A life-cycle toxicity test is conducted to determine what changes in the numbers and weights of individuals of the test species result from effects of the test material on survival, growth, and reproduction. Information might also be obtained on effects of the material on the health and uses of the species.  
5.2 Results of life-cycle tests with mysids might be used to predict long-term effects likely to occur on mysids in field situations as a result of exposure under comparable conditions.  
5.3 Results of life-cycle tests with mysids might be used to compare the chronic sensitivities of different species and the chronic toxicities of different materials, and also to study the effects of various environmental factors on results of such tests.  
5.4 Results of life-cycle tests with mysids might be an important consideration when assessing the hazards of materials to aquatic organisms (see Guide E1023) or when deriving water quality criteria for aquatic organisms (1).4  
5.5 Results of a life-cycle test with mysids might be useful for predicting the results of chronic tests on the same test material with the same species in another water or with another species in the same or a different water (2). Most such predictions take into account results of acute toxicity tests, and so the usefulness of the results from a life-cycle test with mysids is greatly increased by also reporting the results of an acute toxicity test (see Guide E729) conducted under the same conditions.  
5.6 Results of life-cycle tests with mysids might be useful for studying the biological availability of, and structure-activity relationships between, test materials.  
5.7 Results of life-cycle tests with mysids might be useful for predicting population effects on the same species in another water or with another species in the same or a different...
SCOPE
1.1 This guide describes procedures for obtaining laboratory data concerning the adverse effects of a test material added to dilution water, but not to food, on certain species of saltwater mysids during continuous exposure from immediately after birth until after the beginning of reproduction using the flow-through technique. These procedures will probably be useful for conducting life-cycle toxicity tests with other species of mysids, although modifications might be necessary.  
1.2 Other modifications of these procedures might be justified by special needs or circumstances. Although using appropriate procedures is more important than following prescribed procedures, results of tests conducted using unusual procedures are not likely to be comparable to results of many other tests. Comparison of results obtained using modified and unmodified versions of these procedures might provide useful information on new concepts and procedures for conducting life-cycle toxicity tests with saltwater mysids.  
1.3 These procedures are applicable to all chemicals, either individually or in formulations, commercial products, or known mixtures, that can be measured accurately at the necessary concentrations in water. With appropriate modifications, these procedures can be used to conduct tests on temperature, dissolved oxygen, and pH and on such materials as aqueous effluents (see also Guide E1192), leachates, oils, particulate matter, sediments, and surface waters.  
1.4 This guide is arranged as follows:    
Section  
Referenced Documents  
2  
Terminology  
3  
Summary of Guide  
4  
Significance and Use  
5  
Hazards  
7  
Apparatus  
6  
Facilities  
6.1  
Construction Materials  
6.2  
Metering System  
6.3  
Test Chambers  
6.4  
Cleaning  
6.5  
Acceptability  
6.6  
Dilution Water  
8  
Requirements  
8.1  
Source  
8.2  
Treatment  
8.3  
Characterizat...

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ASTM F1686-22(Guide)
Standard Guide for Surveys to Document and Assess Oiling Conditions

SIGNIFICANCE AND USE
3.1 Systematic surveys provide data on shoreline, lakeshore, river bank or other terrain’s character and oiling conditions from which informed planning and operational decisions can be developed with respect to cleanup (1-4).3 In particular, the data are used by decision makers to determine which oiled areas require treatment and to develop end-point criteria for use as targets for the field operations.  
3.2 Surveys may include one or more of four components or phases, as listed below. The scale of an affected area plus quantity and availability of pre-spill information will influence the selection of survey components and its level of detail.  
3.2.1 The aerial reconnaissance survey phase provides a perspective on the overall extent and general nature of the oiling conditions. This information is used in conjunction with environmental, resource, and cultural sensitivity data to guide shoreline protection, recovery of mobile oil, and to facilitate the more detailed response planning and priorities of the response operations.  
3.2.2 The aerial video survey(s) phase provides systematic audio and video documentation of the extent and type of oiling conditions, physical character, and logistics information, such as access and staging data.  
3.2.3 The ground assessment survey(s) phase provides the necessary information and data to develop appropriate response recommendations. A field team(s) collects detailed information on oil conditions, the physical and ecological character of oiled areas, and resources or cultural features that may affect or be affected by the timing or implementation of response activities.  
3.2.4 The post-treatment inspection ground survey or monitoring phase provides the necessary information and data to ensure a segment, that is part of the response program, has been treated to the approved end-point criterion. (5)  
3.3 In order to ensure data consistency, it is important to use standardized terminology and definitions in describing oi...
SCOPE
1.1 This guide covers field procedures by which data can be collected in a systematic manner to document and assess the oiling conditions on shorelines, river banks, and lake shores (shores and substrates) plus dry land habitats (terrain).  
1.2 This guide does not address the terminology that is used to define and describe terrain oiling conditions, the ecological character of oiled terrain, or the cultural or other resources that can be present.  
1.3 The guide is applicable to marine coasts (including estuaries) and to freshwater environments (rivers and lakes) and to dry land habitats. In alignment with Guide F2204:  
1.3.1 For the purpose of this guide, marine and estuarine shorelines, river banks, and lake shores will be collectively referred to as shorelines, shores, or shore-zones.  
1.3.2 Shore types include a range of impermeable (bedrock, ice, and manmade structures), permeable (flats, beaches, and manmade), and coastal wetland (marshes, mangroves) habitats.  
1.4 Other non-shoreline, inland habitats include wetlands (pond, fen, bog, swamp, tundra, and shrub) and drier terrains (grassland, desert, forests), and will be collectively referred to as either wetlands or terrains, respectively.  
1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.  
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 in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barr...

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ASTM F1687-22(Guide)
Standard Guide for Terminology and Indices to Describe Oiling Conditions on Shorelines and Other Terrain

SIGNIFICANCE AND USE
4.1 In order to ensure data consistency, it is important to use standardized terminology and definitions in describing oiling conditions (1)3. This guide provides a template for that purpose.  
4.2 Data on oiling conditions at a shoreline are needed to provide an accurate perspective of the nature and scale of the oiling problem and to facilitate spill-response planning and decision making. Data on oiling conditions would be used in assessing the need for cleanup actions, selecting the most appropriate response technique(s), determining priorities for cleanup, and evaluating the endpoint of cleanup activities.(2-3)  
4.3 Mechanisms by which data are collected can vary (see Guide F1686). They can include aerial video surveys or ground-level assessment surveys. The composition and responsibility of the survey team will depend on the response organization and objectives. The magnitude and type of data sets collected can likewise vary with the nature of the spill and operational needs.  
4.4 Consistent data sets (observations and measurements) on shoreline oiling conditions are essential within any one spill in order to compare the data between different sites or observers, and to compare the data against existing benchmarks or criteria that have been developed to rate the nature or severity of the oiling. To the extent possible, consistency is also desirable between different spills, in order to benefit from previous experiences and cleanup decisions.  
4.5 It is recognized that some modifications may be appropriate based on local or regional geographic conditions or upon the specific character of the stranded oil.
SCOPE
1.1 This guide covers the standardized terminology and types of observational data and indices appropriate to describe the quantity, nature, and distribution of oil and physical oiling conditions on shorelines that have been contaminated by an oil spill.  
1.2 This guide does not address the mechanisms and field procedures by which the necessary data are gathered; nor does it address terminology used to describe the cultural resource or ecological character of oiled shorelines, spill monitoring, or cleanup techniques.  
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.  
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 E2664-22(Practice)
Standard Practice for Methanol Wall Wash of Marine Vessels Handling Polyester Grade Monoethylene Glycol

SIGNIFICANCE AND USE
4.1 The methanol wall wash practice is performed to determine the cleanliness and suitability of cargo tanks or compartments on a marine vessel prior to loading polyester grade monoethylene glycol. Polyester grade monoethylene glycol has very high quality requirements and must be handled with care, as it is adversely affected by oxygen, hydrocarbons, water, and chloride. It is especially susceptible to aromatic contamination, which degrades UV transmittance. Possible sources of contamination are the prior cargoes and cleaning agents. The methanol wall wash procedure provides a representative sampling of the impurities and contamination present on the sides of the cargo tank.
SCOPE
1.1 This practice covers the methanol wall wash procedure for cargo tanks of marine vessels handling polyester grade monoethylene glycol.  
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. For specific hazard statements, see Section 7.  
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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