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ASTM E2115-15

(Guide)

Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied Facilities

Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied Facilities

SIGNIFICANCE AND USE
5.1 This guide is intended to help prevent lead poisoning of children by providing standardized procedures for conducting a lead hazard assessment and providing information needed to develop and recommend lead hazard control options as described in Practice E2252.  
5.2 This guide is applicable for use in either occupied or unoccupied dwellings and in other child-occupied facilities.  
5.3 The procedures in this guide, when supplemented by recommendations for controlling lead hazards, provide for the conduct of a lead risk assessment of a dwelling or of other child-occupied facilities.  
5.4 This guide may be used to supplement assessment procedures used to determine the causes of elevated blood lead (EBL) levels in young children.
Note 2: In cases of EBL levels, investigation of the total living environment of the child and a pediatric medical evaluation may also be needed. Reference should be made to documents such as Managing Elevated Blood Lead Levels Among Young Children,6 Preventing Lead Poisoning in Young Children (1991),7 HUD Technical Guidelines for the Evaluation and Control of Lead-Based Paint Hazards in Housing,5 and Screening Young Children for Lead Poisoning.(1997)7  
5.5 Although this guide was developed for dwellings and for other child-occupied facilities, this guide may be suitable for lead hazard assessments in non-residential buildings and other properties following agreement between assessor and client on appropriate lead action levels.  
5.6 This guide is not intended for use in identifying building materials that when abraded or otherwise degraded, such as that which may occur in remodeling or renovation activities, may result in lead hazards.  
5.7 Lead hazard assessment reports describe lead hazards identified at the time the assessment was performed. The locations, types or severities of lead hazards can change over time as a result of property improvement or deterioration, significant changes in property use, or other factors.
No...
SCOPE
1.1 This guide covers how to conduct, document and report findings of a lead hazard assessment of dwellings and of other child-occupied facilities.  
1.2 Procedures for assessment of personal items, such as toys, dishes, and hobby materials that may contribute to elevated lead levels in blood are not included in this guide.  
1.3 Procedures for random sampling of units within dwellings having multiple units are not included.  
1.4 This guide contains notes, which are explanatory, and are not part of the mandatory requirements of this guide.  
1.5 The values stated in SI units are to be regarded as the 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 and health practices and determine the applicability of regulatory requirements prior to use.

General Information

Status
Historical
Publication Date
30-Apr-2015
ICS
13.040.20 - Ambient atmospheres
Technical Committee
D22 - Air Quality
Drafting Committee
D22.12 - Sampling and Analysis of Lead for Exposure and Risk Assessment
Current Stage
Ref Project

Relations

Replaces
ASTM E2115-06 - Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied Facilities (Withdrawn 2015)
Effective Date
01-May-2015
Referred By
ASTM E2119-20 - Standard Practice for Quality Systems for Conducting In Situ Measurements of Lead Content in Paint or Other Coatings Using Field-Portable X-Ray Fluorescence (XRF) Devices
Effective Date
01-May-2015
Referred By
ASTM E2255/E2255M-22 - Standard Practice for Conducting Visual Assessments for Lead Hazards in Buildings
Effective Date
01-May-2015
Referred By
ASTM E1605-22 - Standard Terminology Relating to Lead in Buildings
Effective Date
01-May-2015
Referred By
ASTM E1729-20 - Standard Practice for Field Collection of Dried Paint Samples for Subsequent Lead Determination
Effective Date
01-May-2015
Referred By
ASTM E1727-20 - Standard Practice for Field Collection of Soil Samples for Subsequent Lead Determination
Effective Date
01-May-2015
Referred By
ASTM E3203-21 - Standard Test Method for Determination of Lead in Dried Paint, Soil, and Wipe Samples by Inductively Coupled Plasma-Optical Emission Spectroscopy (ICP-OES)
Effective Date
01-May-2015
Referred By
ASTM E2252-22 - Standard Practice for Selection of Lead Hazard Reduction Methods for Identified Risks in Residential Housing or Child Occupied Facilities
Effective Date
01-May-2015
Referred By
ASTM E3193-21 - Standard Test Method for Measurement of Lead (Pb) in Dust by Wipe, Paint, and Soil by Flame Atomic Absorption Spectrophotometry (FAAS)
Effective Date
01-May-2015
Referred By
ASTM E1728/E1728M-20 - Standard Practice for Collection of Settled Dust Samples Using Wipe Sampling Methods for Subsequent Lead Determination
Effective Date
01-May-2015

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ASTM E2115-15 - Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied FacilitiesASTM E2115-15 - Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied Facilities
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ASTM E2115-15 - Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied Facilities
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NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.
Contact ASTM International (www.astm.org) for the latest information
Designation: E2115 − 15
Standard Guide for
Conducting Lead Hazard Assessments of Dwellings and of
1
Other Child-Occupied Facilities
This standard is issued under the fixed designation E2115; 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 (ICP-AES), Flame Atomic Absorption Spectrometry
(FAAS), or Graphite Furnace Atomic Absorption Spec-
1.1 This guide covers how to conduct, document and report
trometry (GFAAS) Techniques
findings of a lead hazard assessment of dwellings and of other
E1644 Practice for Hot Plate Digestion of Dust Wipe
child-occupied facilities.
Samples for the Determination of Lead
1.2 Procedures for assessment of personal items, such as
E1645 Practice for Preparation of Dried Paint Samples by
toys, dishes, and hobby materials that may contribute to
Hotplate or Microwave Digestion for Subsequent Lead
elevated lead levels in blood are not included in this guide.
Analysis
1.3 Procedures for random sampling of units within dwell- E1726 Practice for Preparation of Soil Samples by Hotplate
Digestion for Subsequent Lead Analysis
ings having multiple units are not included.
E1727 Practice for Field Collection of Soil Samples for
1.4 This guide contains notes, which are explanatory, and
Subsequent Lead Determination
are not part of the mandatory requirements of this guide.
E1728 PracticeforCollectionofSettledDustSamplesUsing
1.5 The values stated in SI units are to be regarded as the
Wipe Sampling Methods for Subsequent Lead Determi-
standard.
nation
1.6 This standard does not purport to address all of the E1729 Practice for Field Collection of Dried Paint Samples
safety concerns, if any, associated with its use. It is the for Subsequent Lead Determination
responsibility of the user of this standard to establish appro- E1753 Practice for Use of Qualitative Chemical Spot Test
priate safety and health practices and determine the applica- Kits for Detection of Lead in Dry Paint Films
bility of regulatory requirements prior to use. E1979 Practice for Ultrasonic Extraction of Paint, Dust,
Soil, and Air Samples for Subsequent Determination of
2. Referenced Documents
Lead
2
E2051 Practice for the Determination of Lead in Paint,
2.1 ASTM Standards:
Settled Dust, Soil and Air Particulate by Field-Portable
D4840 Guide for Sample Chain-of-Custody Procedures
3
Electroanalysis (Withdrawn 2010)
E631 Terminology of Building Constructions
E2119 Practice for Quality Systems for Conducting In Situ
E1605 Terminology Relating to Lead in Buildings
Measurements of Lead Content in Paint or Other Coatings
E1613 Test Method for Determination of Lead by Induc-
Using Field-Portable X-Ray Fluorescence (XRF) Devices
tively Coupled Plasma Atomic Emission Spectrometry
E2239 PracticeforRecordKeepingandRecordPreservation
for Lead Hazard Activities
1
This guide is under the jurisdiction of ASTM Committee D22 on Air Quality
E2252 Practice for Selection of Lead Hazard Reduction
and is the direct responsibility of Subcommittee D22.12 on Sampling andAnalysis,
Methods for Identified Risks in Residential Housing or
of Lead, for Exposure and Risk Assessment.
Child Occupied Facilities
CurrenteditionapprovedMay1,2015.PublishedJuly2015.Originallyapproved
in 2000. Last previous edition approved in 2006 as E2115 – 06 which was
E2255/E2255M Practice for ConductingVisualAssessments
withdrawn January 2015 and reinstated in May 2015. DOI: 10.1520/E2115-15.
for Lead Hazards in Buildings
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
3
Standards volume information, refer to the standard’s Document Summary page on The last approved version of this historical standard is referenced on
the ASTM website. www.astm.org.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 ----------------------
E2115 − 15
6
Elevated Blood Lead Levels Among Young Children, Preventing Lead
2.2 Other Documents:
7
Poisoning in Young Children (1991), HUD Technical Guidelines for the
40 CFR 745, Environmental Protection Agency (EPA),
5
Evaluation and Control of Lead-Based Paint Hazards in Housing, and
Lead-Based Paint Poisoning Prevention in Certain Resi-
7
Screening Young Children for Lead Poisoning.(1997)
4
dential Structures (especially subparts D, L and Q)
5.5 Although this guide was developed for dwellings and
Guidelines for the Evaluation and Control of Lead-Based
for other child-occupied facilities, this guide may be suitable
Paint Hazards in Housing, 2nd Ed
...

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5.1 This test method is intended for use with other standards that address the collection and preparation of samples (airborne particulate, dusts by wipe and micro-vacuuming, dried paint chips, and soils) that are obtained during the assessment or mitigation of lead hazards from buildings and related structures.  
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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.  
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1.2 This guide has been designed with flexibility to allow expansion to address various characterizations of atmospheric dispersion, which might involve dose or concentration fluctuations, to allow development of application-specific evaluation schemes, and to allow use of various statistical comparison metrics. No assumptions are made regarding the manner in which the models characterize the dispersion.  
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1.5 This standard applies to gaussian plume models; it may not be applicable to non-point sources, heavy gas models from evaporation from pool (for example, liquid spills), as well as near-field receptors.  
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ASTM D7440-23(Practice)
Standard Practice for Characterizing Uncertainty in Air Quality Measurements

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6.1 A primary use intended for this practice is for qualifying ASTM International Standards as Standard Test Methods. In the past, a “Precision and Bias” report has been required. However, recently a statement of uncertainty has become an acceptable alternative to Guide D3670. Inclusion of such a statement with a method description simplifies comparison of ASTM Test Methods to analogous ISO and Committee for European Normalization (CEN) standards, now required to have uncertainty statements.  
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ASTM D7520-16(2023)(Test Method)
Standard Test Method for Determining the Opacity of a Plume in the Outdoor Ambient Atmosphere

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5.1 Air permits from regulatory agencies often require measurements of opacity from stationary air pollution point sources in the outdoor ambient environment. Opacity has been visually measured by certified smoke readers in accordance with USEPA (USEPA Method 9). DCOT is also a method to determine plume opacity in the outdoor ambient environment.  
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1.2 This practice is based on the sorption of VOCs from air onto selected sorbents or combinations of sorbents. Sampled air is either drawn through a tube containing one or a series of sorbents (pumped sampling) or allowed to diffuse, under controlled conditions, onto the sorbent surface at the sampling end of the tube (diffusive or passive sampling). The sorbed VOCs are subsequently recovered by thermal desorption and analyzed by capillary gas chromatography.  
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4.1 This practice is intended for the collection of airborne fungal spores or fragments, or both, using inertial impaction.  
4.2 It is the responsibility of the user to assure that they are in compliance with all local, state and federal regulations governing the inspection of buildings for fungal colonization and the collection of associated samples.  
4.3 This practice is intended to provide the user with a basic understanding of the equipment, materials and instructions necessary to effectively collect air samples using an inertial impactor.  
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1.1 The purpose of this practice is to describe procedures for the collection of airborne fungal spores or fragments, or both, using inertial impaction sampling techniques.  
1.2 This practice is not intended to limit the user from the collection of other airborne particulates that may be of interest and captured through this technique.  
1.3 This practice presumes that the user has a fundamental understanding of field investigative techniques related to the scientific process, and sampling plan development and implementation. It is important to establish the related hypothesis to be tested and the supporting analytical methodology needed in order to identify the sampling media to be used and the laboratory conditions for analysis.  
1.4 This practice does not address the development of a formal hypothesis or the establishment of appropriate and defensible investigation and sampling objectives. It is presumed the investigator has the experience and knowledge base to address these issues.  
1.5 This practice does not provide the user sufficient information to allow for interpretation of the analytical results from sample collection. It is the user's responsibility to seek or obtain the information and knowledge necessary to interpret the sample results reported by the laboratory.  
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.  
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ASTM E2115-22(Guide)
Standard Guide for Conducting Lead Hazard Assessments of Dwellings and of Other Child-Occupied Facilities

SIGNIFICANCE AND USE
5.1 This guide is intended to help prevent lead poisoning of children by providing standardized procedures for conducting a lead hazard assessment and providing information needed to develop and recommend lead hazard control options as described in Practice E2252.  
5.2 This guide is applicable for use in either occupied or unoccupied dwellings and in other child-occupied facilities.  
5.3 The procedures in this guide, when supplemented by recommendations for controlling lead hazards, provide for the conduct of a lead risk assessment of a dwelling or of other child-occupied facilities.  
5.4 This guide may be used to supplement assessment procedures used to determine the causes of elevated blood lead (EBL) levels in young children.
Note 2: In cases of EBL levels, investigation of the total living environment of the child and a pediatric medical evaluation may also be needed. Reference should be made to documents such as Managing Elevated Blood Lead Levels Among Young Children,6 Preventing Lead Poisoning in Young Children (1991),7 the HUD Guidelines, and Screening Young Children for Lead Poisoning (1997).7  
5.5 Although this guide was developed for dwellings and for other child-occupied facilities, this guide may be suitable for lead hazard assessments in non-residential buildings and other properties following agreement between assessor and client on appropriate lead action levels.  
5.6 This guide is not intended for use in identifying building materials that when abraded or otherwise degraded, such as that which may occur in remodeling or renovation activities, may result in lead hazards.  
5.7 Lead hazard assessment reports describe lead hazards identified at the time the assessment was performed. The locations, types, or severities of lead hazards can change over time as a result of property improvement or deterioration, significant changes in property use, or other factors.
Note 3: The term “lead-free” should never be used to describe the absence of ...
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1.1 This guide covers how to conduct, document, and report findings of a lead hazard assessment of dwellings and of other child-occupied facilities.  
1.2 Procedures for assessment of personal items, such as toys, dishes, and hobby materials that may contribute to elevated lead levels in blood are not included in this guide.  
1.3 Procedures for random sampling of units within dwellings having multiple units are not included.  
1.4 This guide contains notes, which are explanatory, and are not part of the mandatory requirements of this guide.  
1.5 The values stated in SI units are to be regarded as the standard.  
1.5.1 Exception—The inch-pound and SI units shown for wipe sampling data are to be individually regarded as standard for wipe sampling data.  
1.6 Methods described in this guide may not meet or be allowed by requirements or regulations established by local authorities having jurisdiction. It is the responsibility of the user of this standard to comply with all such requirements and regulations.  
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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Standard Practice for Performance Evaluation of Ambient Outdoor Air Quality Sensors and Sensor-based Instruments for Portable and Fixed-point Measurement

SIGNIFICANCE AND USE
5.1 This practice establishes standardized tests for the performance evaluation of sensor-based continuous instruments for ambient air quality measurements. Public and private air monitoring interests have manifested themselves as a driving force for the deployment of air quality sensors and instruments to quantify air pollutant concentrations in communities, around schools, around industrial facilities, and elsewhere. Users of air quality sensors require information on the performance and limitations of these devices so that informed decisions regarding their suitability for various purposes can be determined. This practice describes both laboratory and field tests that provide information on candidate instrument repeatability, sensitivity, linearity, cross-interferences, drift and comparability with more costly instruments typically used by entities such as government agencies. The air quality sensors are first evaluated in a laboratory chamber by comparing their response to a reference instrument and challenging the gas sensors with interferents. The sensors are then deployed outdoors for field testing at two sites with different climates against reference air quality instruments. This practice is intended to be referenced in standards and codes that establish minimum performance quality for sensor-based ambient outdoor air monitoring.  
5.2 This practice is intended for air quality sensors that measure one or more of the criteria pollutants in ambient air (ozone, carbon monoxide, nitrogen dioxide, sulfur dioxide, PM10 and PM2.5) that can be operated in outdoor environments and can log a concentration reading. It is not intended for devices or transducers that require additional enclosures for deployment outdoors or post-processing to convert their output signal into a pollutant concentration reading.  
5.3 It is anticipated that the main users of this practice will be manufacturers, developers, and distributors of outdoor air quality sensors, air quality agenc...
SCOPE
1.1 This practice establishes standardized tests for the performance evaluation of sensor-based continuous instruments for ambient outdoor air quality measurements. It describes both laboratory and field tests that provide information on candidate sensor repeatability, sensitivity, linearity, cross-interferences, drift, and comparability against reference instruments.  
1.2 This practice does not apply to sensors or instruments that remotely measure atmospheric pollutants using open path, lidar, or imaging technology.  
1.3 The evaluation procedures contained in this practice are for sensors that alone or in combination measure outdoor criteria pollutants in ambient air: particulate matter (PM2.5 and PM10), sulfur dioxide (SO2), ozone (O3), carbon monoxide (CO), or nitrogen dioxide (NO2) at concentrations that are relevant to public health.  
1.4 Testing is to be performed by a competent entity able to demonstrate that it operates in conformity with internationally accepted test laboratory quality standards such as ISO/IEC 17025.  
1.5 Units—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 Barriers to Trade (TBT) Committee.

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ASTM
ASTM D1914-95(2022)(Practice)
Standard Practice for Conversion Units and Factors Relating to Sampling and Analysis of Atmospheres

SIGNIFICANCE AND USE
3.1 ASTM requires the use of SI units in all its publications and their use in reporting atmospheric measurement data. However, there are historic data and even data currently reported that are based on a variety of units of measurement. This practice tabulates factors that are necessary to convert such data to SI and other units of measurement.  
3.2 IEEE/ASTM SI-10 does not list all the conversion factors commonly used in air pollution and meteorological fields. This practice supplements IEEE/ASTM SI-10.  
3.3 The values reported here were obtained from a number of standard publications. They were adjusted to five figures and organized in a rational order. All values reflect the latest information from the 16th General Conference on Weights and Measurements held in 1979.  
3.4 The factors in Table 1 are provided to change units of measurement from one system to related units in other systems, as well as to smaller or larger units in the same system.  
3.5 Values of units in the left column may be converted to values of units in the right column merely by multiplying by the conversion factor provided in the center column.  (A) For specific applications and exceptions, see Terminology D1356.
SCOPE
1.1 This practice provides units and factors useful for members of the air pollution and meteorological communities.  
1.2 This practice is used together with IEEE/ASTM SI-10, which discusses SI units and contains selected conversion factors for inter-relation of SI units and some commonly used non-metric units.  
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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ASTM
ASTM D2914-15(2022)(Test Method)
Standard Test Methods for Sulfur Dioxide Content of the Atmosphere (West-Gaeke Method)

SIGNIFICANCE AND USE
5.1 Sulfur dioxide is a major air pollutant, commonly formed by the combustion of sulfur-bearing fuels. The Environmental Protection Agency (EPA) has set primary and secondary air quality standards (7) that are designed to protect the public health and welfare.  
5.2 The Occupational Safety and Health Administration (OSHA) has promulgated exposure limits for sulfur dioxide in workplace atmospheres (8).  
5.3 These methods have been found satisfactory for measuring sulfur dioxide in ambient and workplace atmospheres over the ranges pertinent in 5.1 and 5.2.  
5.4 Method A has been designed to correspond to the EPA-Designated Reference Method (7) for the determination of sulfur dioxide.
SCOPE
1.1 These test methods cover the bubbler collection and colorimetric determination of sulfur dioxide (SO2) in the ambient or workplace atmosphere.  
1.2 These test methods are applicable for determining SO2 over the range from approximately 25 μg/m3 (0.01 ppm(v)) to 1000 μg/m3 (0.4 ppm(v)), corresponding to a solution concentration of 0.03 μg SO2/mL to 1.3 μg SO2/mL. Beer's law is followed through the working analytical range from 0.02 μg SO2/mL to 1.4 μg SO2/mL.  
1.3 The lower limit of detection is 0.075 μg SO2/mL (1),2 representing an air concentration of 25 μg SO2/m3 (0.01 ppm(v)) in a 30-min sample, or 13 μg SO2/m3 (0.005 ppm(v)) in a 24-h sample.  
1.4 These test methods incorporate sampling for periods between 30 min and 24 h.  
1.5 These test methods describe the determination of the collected (impinged) samples. A Method A and a Method B are described.  
1.6 Method A is preferred over Method B, as it gives the higher sensitivity, but it has a higher blank. Manual Method B is pH-dependent, but is more suitable with spectrometers having a spectral band width greater than 20 nm.
Note 1: These test methods are applicable at concentrations below 25 μg/m3 by sampling larger volumes of air if the absorption efficiency of the particular system is first determined, as described in Annex A4.
Note 2: Concentrations higher than 1000 μg/m3 can be determined by using smaller gas volumes, larger collection volumes, or by suitable dilution of the collected sample with absorbing solution prior to analysis.  
1.7 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.  
1.8 Warning—Mercury has been designated by many regulatory agencies as a hazardous material that can cause serious medical issues. Mercury, or its vapor, has been demonstrated to be hazardous to health and corrosive to materials. Caution should be taken when handling mercury and mercury containing products. See the applicable product Safety Data Sheet (SDS) for additional information. Users should be aware that selling mercury and/or mercury containing products into your state or country may be prohibited by law.  
1.9 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 precautionary statements, see 8.3.1, Section 9, and A3.1.3.  
1.10 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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