Standard Guide for NAPL Mobility and Migration in Sediments – Screening Process to Categorize Samples for Laboratory NAPL Mobility Testing

SIGNIFICANCE AND USE
4.1 NAPLs (for example, chlorinated solvents, petroleum products, and creosote) can be emplaced in sediments through a variety of mechanisms (Guide E3248). Dense non-aqueous phase liquids (DNAPLs) are more dense than water, whereas light non-aqueous phase liquids (LNAPLs) are less dense than water.  
4.2 Standardized guidance and test methods currently exist for assessing NAPL mobility at upland sites, from organizations such as ASTM (Guides E2531 and E2856), Interstate Technology & Regulatory Council (1)3 and the American Petroleum Institute (2, 3).  
4.3 Guide E3248 provides guidance regarding when a NAPL movement evaluation is warranted. After confirming that NAPL is present and evaluating nature and extent as appropriate, the next step in any NAPL movement evaluation is to evaluate if NAPL is mobile or immobile at the pore scale—this is done using tiered or weight of evidence (WOE) approaches. This guide provides a structured process to select samples to submit to the laboratory for NAPL mobility testing that is part of a NAPL movement evaluation.  
4.4 This guide may be used by various parties involved in sediment corrective action programs, including regulatory agencies, project sponsors, environmental consultants, toxicologists, risk assessors, site remediation professionals, environmental contractors, and other stakeholders.  
4.5 This guide should be used in conjunction with other reference material (refer to Section 2 and References) that direct the user in developing and implementing sediment assessment programs.  
4.6 This guide is related to Guide E3163, concerning sediment analytical techniques used during sediment programs. This relates to Guide E3248, which discusses generic models for the emplacement and advection of NAPL in sediments. It is related to Guide E3268, which describes sample collection, field screening and sample handling considerations in NAPL movement evaluations. And this is related to Guide E3282, which describes evaluation met...
SCOPE
1.1 This guide is designed for general application at a wide range of sediment sites where non-aqueous phase liquid (NAPL) is present or suspected to be present in the sediment. This guide describes a process to use field screening methods, specifically visual observations, and the results of shake tests, to categorize the relative amount of NAPL present in a sample. This categorization can then be utilized to select co-located sediment samples for laboratory testing to determine if the NAPL in the sample interval is mobile or immobile at the pore scale, or any other chemical or physical testing.  
1.1.1 There is no current industry standard methodology to select sediment samples for laboratory NAPL mobility testing; the use of different methodologies is possible. This guide focuses on a selection process that uses visual observations and shake tests. This process has the advantage of being simple to use and, if applied in a disciplined manner, has been demonstrated to provide good results in the field.  
1.2 This guide is intended to inform, complement, and support characterization and remedial efforts performed under international, federal, state, and local environmental programs but not supersede local, state, federal, or international regulations. The users of this guide should review existing information and data available for a sediment site to determine applicable regulatory agency requirements and the most appropriate entry point into and use of this guide.  
1.3 ASTM International (ASTM) standard guides are not regulations; they are consensus standard guides that may be followed voluntarily to support applicable regulatory requirements. This guide may be used in conjunction with other ASTM guides developed for assessing sediment sites.  
1.4 This guide does not address methods and means of sample collection (Guide E3163).  
1.5 Units—The values stated in SI or CGS units are to be regarded as the standard. N...

General Information

Status
Published
Publication Date
30-Sep-2021
Drafting Committee
E50.04 - Corrective Action

Relations

Effective Date
01-Apr-2020
Effective Date
01-Sep-2018
Effective Date
15-Dec-2017
Effective Date
15-Dec-2017
Effective Date
15-Jul-2017
Effective Date
01-Oct-2012
Effective Date
01-Jan-2012
Effective Date
01-Nov-2011
Effective Date
01-Nov-2011
Effective Date
01-Jul-2011
Effective Date
01-May-2011
Effective Date
01-Jan-2010
Effective Date
15-Jun-2009
Effective Date
15-May-2009
Effective Date
01-Nov-2006

Overview

ASTM E3281-21a, "Standard Guide for NAPL Mobility and Migration in Sediments – Screening Process to Categorize Samples for Laboratory NAPL Mobility Testing," provides structured guidance for evaluating the presence and mobility of non-aqueous phase liquids (NAPLs) in sediment environments. The guide is broadly applicable to sites where NAPLs-such as petroleum products, chlorinated solvents, or creosote-are present or suspected in sediments. Its primary objective is to support environmental site assessments, corrective action programs, and remediation strategies by establishing a consistent screening and sample selection methodology using visual observations and shake tests. Employing these standardized processes ensures improved data comparability and efficiency when identifying locations for laboratory NAPL mobility testing.

Key Topics

  • NAPL Types and Behavior: The standard defines NAPLs as chemicals that exist as a separate phase due to low solubility in water. It distinguishes between Light NAPLs (LNAPLs, less dense than water) and Dense NAPLs (DNAPLs, denser than water), each requiring different assessment considerations.
  • Screening Methodology: The guide outlines a four-step process:
    • Field visual observation for sheen or visible NAPL in sediment samples.
    • Confirmatory sediment-water shake tests to detect and categorize NAPL presence.
    • Categorization of samples based on the relative NAPL amount, establishing four categories from "no NAPL" to "high NAPL presence."
    • Sample selection for lab testing, focusing on targeted locations and depths for determining NAPL mobility or immobility at the pore scale.
  • Data Consistency and Documentation: Procedures are provided for systematically recording results, including visual observation logs, shake test documentation, and photographic evidence, helping reduce variability across field teams and investigations.

Applications

The ASTM E3281-21a standard guide delivers practical value in a range of environmental programs and sediment site investigations involving NAPL contamination:

  • Environmental Site Assessment: Enables efficient and reproducible screening of sediment cores and grab samples to determine where mobile NAPL may pose a risk.
  • Remediation Planning: Assists project teams in selecting representative sediment samples for laboratory mobility testing, supporting effective remedial action designs.
  • Regulatory Compliance: Aligns site investigations with international, federal, state, and local requirements while complementing existing regulatory programs.
  • Stakeholder Engagement: Provides a transparent and standardized approach beneficial for communication among regulatory agencies, site owners, consultants, contractors, toxicologists, and environmental professionals.
  • Field Efficiency: Facilitates rapid and cost-effective identification of areas with higher NAPL concentrations, focusing laboratory analyses where they are most needed.
  • Data Comparability: Standardized screening methods support consistent reporting, critical for multi-party or long-term project contexts.

Related Standards

ASTM E3281-21a is designed for use alongside several other ASTM and industry standards relevant to NAPL characterization in sediments:

  • ASTM E3163 – Selection and Application of Analytical Methods during Sediment Corrective Action
  • ASTM E3248 – Conceptual Models for NAPL Emplacement and Advection in Sediment
  • ASTM E3268 – Sample Collection, Field Screening, and Handling in NAPL Evaluations
  • ASTM E3282 – Evaluation Metrics for NAPL Mobility and Migration
  • ASTM E2531/E2856 – Guidance on LNAPL site characterization and transmissivity estimation
  • ASTM D2487/D2488 – Soil classification and identification for engineering purposes

Conclusion

ASTM E3281-21a offers an essential, standardized framework for environmental professionals evaluating NAPL mobility in sediments. Its screening and categorization methodology, based on visual and shake test observations, facilitates robust sample selection for laboratory testing. As a consensus standard, it enhances the defensibility, consistency, and regulatory relevance of sediment NAPL assessments, thereby supporting effective risk management and remediation at contaminated sites.

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Frequently Asked Questions

ASTM E3281-21a is a guide published by ASTM International. Its full title is "Standard Guide for NAPL Mobility and Migration in Sediments – Screening Process to Categorize Samples for Laboratory NAPL Mobility Testing". This standard covers: SIGNIFICANCE AND USE 4.1 NAPLs (for example, chlorinated solvents, petroleum products, and creosote) can be emplaced in sediments through a variety of mechanisms (Guide E3248). Dense non-aqueous phase liquids (DNAPLs) are more dense than water, whereas light non-aqueous phase liquids (LNAPLs) are less dense than water. 4.2 Standardized guidance and test methods currently exist for assessing NAPL mobility at upland sites, from organizations such as ASTM (Guides E2531 and E2856), Interstate Technology & Regulatory Council (1)3 and the American Petroleum Institute (2, 3). 4.3 Guide E3248 provides guidance regarding when a NAPL movement evaluation is warranted. After confirming that NAPL is present and evaluating nature and extent as appropriate, the next step in any NAPL movement evaluation is to evaluate if NAPL is mobile or immobile at the pore scale—this is done using tiered or weight of evidence (WOE) approaches. This guide provides a structured process to select samples to submit to the laboratory for NAPL mobility testing that is part of a NAPL movement evaluation. 4.4 This guide may be used by various parties involved in sediment corrective action programs, including regulatory agencies, project sponsors, environmental consultants, toxicologists, risk assessors, site remediation professionals, environmental contractors, and other stakeholders. 4.5 This guide should be used in conjunction with other reference material (refer to Section 2 and References) that direct the user in developing and implementing sediment assessment programs. 4.6 This guide is related to Guide E3163, concerning sediment analytical techniques used during sediment programs. This relates to Guide E3248, which discusses generic models for the emplacement and advection of NAPL in sediments. It is related to Guide E3268, which describes sample collection, field screening and sample handling considerations in NAPL movement evaluations. And this is related to Guide E3282, which describes evaluation met... SCOPE 1.1 This guide is designed for general application at a wide range of sediment sites where non-aqueous phase liquid (NAPL) is present or suspected to be present in the sediment. This guide describes a process to use field screening methods, specifically visual observations, and the results of shake tests, to categorize the relative amount of NAPL present in a sample. This categorization can then be utilized to select co-located sediment samples for laboratory testing to determine if the NAPL in the sample interval is mobile or immobile at the pore scale, or any other chemical or physical testing. 1.1.1 There is no current industry standard methodology to select sediment samples for laboratory NAPL mobility testing; the use of different methodologies is possible. This guide focuses on a selection process that uses visual observations and shake tests. This process has the advantage of being simple to use and, if applied in a disciplined manner, has been demonstrated to provide good results in the field. 1.2 This guide is intended to inform, complement, and support characterization and remedial efforts performed under international, federal, state, and local environmental programs but not supersede local, state, federal, or international regulations. The users of this guide should review existing information and data available for a sediment site to determine applicable regulatory agency requirements and the most appropriate entry point into and use of this guide. 1.3 ASTM International (ASTM) standard guides are not regulations; they are consensus standard guides that may be followed voluntarily to support applicable regulatory requirements. This guide may be used in conjunction with other ASTM guides developed for assessing sediment sites. 1.4 This guide does not address methods and means of sample collection (Guide E3163). 1.5 Units—The values stated in SI or CGS units are to be regarded as the standard. N...

SIGNIFICANCE AND USE 4.1 NAPLs (for example, chlorinated solvents, petroleum products, and creosote) can be emplaced in sediments through a variety of mechanisms (Guide E3248). Dense non-aqueous phase liquids (DNAPLs) are more dense than water, whereas light non-aqueous phase liquids (LNAPLs) are less dense than water. 4.2 Standardized guidance and test methods currently exist for assessing NAPL mobility at upland sites, from organizations such as ASTM (Guides E2531 and E2856), Interstate Technology & Regulatory Council (1)3 and the American Petroleum Institute (2, 3). 4.3 Guide E3248 provides guidance regarding when a NAPL movement evaluation is warranted. After confirming that NAPL is present and evaluating nature and extent as appropriate, the next step in any NAPL movement evaluation is to evaluate if NAPL is mobile or immobile at the pore scale—this is done using tiered or weight of evidence (WOE) approaches. This guide provides a structured process to select samples to submit to the laboratory for NAPL mobility testing that is part of a NAPL movement evaluation. 4.4 This guide may be used by various parties involved in sediment corrective action programs, including regulatory agencies, project sponsors, environmental consultants, toxicologists, risk assessors, site remediation professionals, environmental contractors, and other stakeholders. 4.5 This guide should be used in conjunction with other reference material (refer to Section 2 and References) that direct the user in developing and implementing sediment assessment programs. 4.6 This guide is related to Guide E3163, concerning sediment analytical techniques used during sediment programs. This relates to Guide E3248, which discusses generic models for the emplacement and advection of NAPL in sediments. It is related to Guide E3268, which describes sample collection, field screening and sample handling considerations in NAPL movement evaluations. And this is related to Guide E3282, which describes evaluation met... SCOPE 1.1 This guide is designed for general application at a wide range of sediment sites where non-aqueous phase liquid (NAPL) is present or suspected to be present in the sediment. This guide describes a process to use field screening methods, specifically visual observations, and the results of shake tests, to categorize the relative amount of NAPL present in a sample. This categorization can then be utilized to select co-located sediment samples for laboratory testing to determine if the NAPL in the sample interval is mobile or immobile at the pore scale, or any other chemical or physical testing. 1.1.1 There is no current industry standard methodology to select sediment samples for laboratory NAPL mobility testing; the use of different methodologies is possible. This guide focuses on a selection process that uses visual observations and shake tests. This process has the advantage of being simple to use and, if applied in a disciplined manner, has been demonstrated to provide good results in the field. 1.2 This guide is intended to inform, complement, and support characterization and remedial efforts performed under international, federal, state, and local environmental programs but not supersede local, state, federal, or international regulations. The users of this guide should review existing information and data available for a sediment site to determine applicable regulatory agency requirements and the most appropriate entry point into and use of this guide. 1.3 ASTM International (ASTM) standard guides are not regulations; they are consensus standard guides that may be followed voluntarily to support applicable regulatory requirements. This guide may be used in conjunction with other ASTM guides developed for assessing sediment sites. 1.4 This guide does not address methods and means of sample collection (Guide E3163). 1.5 Units—The values stated in SI or CGS units are to be regarded as the standard. N...

ASTM E3281-21a is classified under the following ICS (International Classification for Standards) categories: 13.080.01 - Soil quality and pedology in general. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM E3281-21a has the following relationships with other standards: It is inter standard links to ASTM E3248-20, ASTM E3163-18, ASTM D2487-17, ASTM D2487-17e1, ASTM D2488-17, ASTM E2856-12, ASTM F2534-12, ASTM E2856-11e1, ASTM E2856-11, ASTM D7203-11, ASTM D2487-11, ASTM D2487-10, ASTM D2488-09a, ASTM D2488-09, ASTM D2488-06. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM E3281-21a is available in PDF format for immediate download after purchase. The document can be added to your cart and obtained through the secure checkout process. Digital delivery ensures instant access to the complete standard document.

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: E3281 − 21a
Standard Guide for
NAPL Mobility and Migration in Sediments – Screening
Process to Categorize Samples for Laboratory NAPL
Mobility Testing
This standard is issued under the fixed designation E3281; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision.Anumber in parentheses indicates the year of last reapproval.A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope 1.5 Units—The values stated in SI or CGS units are to be
regarded as the standard. No other units of measurement are
1.1 This guide is designed for general application at a wide
included in this standard.
range of sediment sites where non-aqueous phase liquid
1.6 This standard does not purport to address all of the
(NAPL) is present or suspected to be present in the sediment.
safety concerns, if any, associated with its use. It is the
This guide describes a process to use field screening methods,
responsibility of the user of this standard to establish appro-
specifically visual observations, and the results of shake tests,
priate safety, health, and environmental practices and deter-
tocategorizetherelativeamountofNAPLpresentinasample.
mine the applicability of regulatory limitations prior to use.
This categorization can then be utilized to select co-located
1.7 This international standard was developed in accor-
sediment samples for laboratory testing to determine if the
dance with internationally recognized principles on standard-
NAPLin the sample interval is mobile or immobile at the pore
ization established in the Decision on Principles for the
scale, or any other chemical or physical testing.
Development of International Standards, Guides and Recom-
1.1.1 There is no current industry standard methodology to
mendations issued by the World Trade Organization Technical
select sediment samples for laboratory NAPLmobility testing;
Barriers to Trade (TBT) Committee.
the use of different methodologies is possible. This guide
focusesonaselectionprocessthatusesvisualobservationsand
2. Referenced Documents
shake tests. This process has the advantage of being simple to
2.1 ASTM Standards:
use and, if applied in a disciplined manner, has been demon-
D2487Practice for Classification of Soils for Engineering
strated to provide good results in the field.
Purposes (Unified Soil Classification System)
1.2 This guide is intended to inform, complement, and
D2488Practice for Description and Identification of Soils
support characterization and remedial efforts performed under
(Visual-Manual Procedures)
international, federal, state, and local environmental programs
D7203Practice for Screening Trichloroethylene (TCE)-
but not supersede local, state, federal, or international regula-
Contaminated Media Using a Heated Diode Sensor
tions. The users of this guide should review existing informa-
E2531Guide for Development of Conceptual Site Models
tion and data available for a sediment site to determine
and Remediation Strategies for Light Nonaqueous-Phase
applicableregulatoryagencyrequirementsandthemostappro-
Liquids Released to the Subsurface
priate entry point into and use of this guide.
E2856Guide for Estimation of LNAPL Transmissivity
1.3 ASTM International (ASTM) standard guides are not
E3163Guide for Selection and Application of Analytical
regulations; they are consensus standard guides that may be
Methods and Procedures Used during Sediment Correc-
followed voluntarily to support applicable regulatory require-
tive Action
ments. This guide may be used in conjunction with other
E3248GuideforNAPLMobilityandMigrationinSediment
ASTM guides developed for assessing sediment sites.
–Conceptual Models for Emplacement and Advection
E3268 Guide for NAPL Mobility and Migration in
1.4 This guide does not address methods and means of
Sediment—Sample Collection, Field Screening, and
sample collection (Guide E3163).
Sample Handling
E3282Guide for NAPL Mobility and Migration in Sedi-
ments – Evaluation Metrics
ThisguideisunderthejurisdictionofASTMCommitteeE50onEnvironmental
Assessment, Risk Management and CorrectiveAction and is the direct responsibil-
ity of Subcommittee E50.04 on Corrective Action. For referenced ASTM standards, visit the ASTM website, www.astm.org, or
Current edition approved Oct. 1, 2021. Published November 2021. Originally contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
approved in 2021. Last previous edition approved in 2021 as E3281–21. DOI: Standards volume information, refer to the standard’s Document Summary page on
10.1520/E3281–21A the ASTM website.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
E3281 − 21a
F2534Guide for Visually Estimating Oil Spill Thickness on agencies, project sponsors, environmental consultants,
Water toxicologists, risk assessors, site remediation professionals,
environmental contractors, and other stakeholders.
3. Terminology
4.5 This guide should be used in conjunction with other
3.1 Definitions:
reference material (refer to Section 2 and References) that
3.1.1 immobile NAPL, n—NAPL that does not move by
direct the user in developing and implementing sediment
advection within the connected void spaces of the sediment
assessment programs.
under specified physical and chemical conditions, as may be
4.6 This guide is related to Guide E3163, concerning
demonstrated by laboratory testing, or may be interpreted
sedimentanalyticaltechniquesusedduringsedimentprograms.
based on mathematical calculations or modeling. E3248
This relates to Guide E3248, which discusses generic models
3.1.2 mobile NAPL, n—NAPLthat may move by advection
fortheemplacementandadvectionofNAPLinsediments.Itis
withintheconnectedvoidspacesofthesedimentunderspecific
related to Guide E3268, which describes sample collection,
physical and chemical conditions, as may be demonstrated by
field screening and sample handling considerations in NAPL
laboratory testing, or as may be interpreted based on math-
movement evaluations. And this is related to Guide E3282,
ematical calculations or modeling. E3248
which describes evaluation metrics and frameworks to deter-
mine if NAPLis immobile or immobile at the pore scale, or if
3.1.3 non-aqueous phase liquid, NAPL, n—chemicals that
are insoluble or only slightly soluble in water that exist as a it is migrating or stable at the NAPL body scale.
separate liquid phase in environmental media. E3248
4.7 This guide does not replace the need for engaging
3.1.3.1 Discussion—NAPL may be less dense than water
competent persons to evaluate NAPLemplacement and move-
(light non-aqueous phase liquid [LNAPL]) or more dense than
ment in sediments. Activities necessary to develop a concep-
water (dense non-aqueous phase liquid [DNAPL]).
tual site model should be conducted by persons familiar with
3.1.4 pore scale, n—the scale of the connected void spaces NAPL-impacted sediment site characterization techniques,
within the sediment. E3248 physical and chemical properties of NAPL in sediments, fate
and transport processes, remediation technologies, and sedi-
3.1.5 sediment(s), n—a matrix of pore water and particles
ment evaluation protocols. The users of this guide should
including gravel, sand, silt, clay, and other natural and anthro-
consider assembling a team of experienced project profession-
pogenic substances that have settled at the bottom of a tidal or
als with appropriate expertise to scope, plan, and execute
nontidal body of water. E3163
sediment NAPL data acquisition activities.
3.1.6 sheen, n—a silvery, rainbow, or dark rainbow film on
4.8 This guide provides a framework based on overarching
the surface of the sediment sample or on a water surface.
features and elements that should be customized by the user,
4. Significance and Use based on site-specific conditions, regulatory context, and
program objectives for a particular sediment site. This guide
4.1 NAPLs (for example, chlorinated solvents, petroleum
should not be used alone as a prescriptive checklist.
products, and creosote) can be emplaced in sediments through
4.9 The user of this guide should review the overall struc-
a variety of mechanisms (Guide E3248). Dense non-aqueous
ture and components of this guide before proceeding with use,
phase liquids (DNAPLs) are more dense than water, whereas
including:
light non-aqueous phase liquids (LNAPLs) are less dense than
water.
Section 1 Scope
Section 2 Referenced Documents
4.2 Standardized guidance and test methods currently exist
Section 3 Terminology
Section 4 Significance and Use
for assessing NAPL mobility at upland sites, from organiza-
Section 5 Summary of the Process for Screening and Selection of
tions such as ASTM (Guides E2531 and E2856), Interstate
Samples for Laboratory NAPL Mobility Testing
Technology & Regulatory Council (1) and the American
Section 6 Methods for Recording Visual Observations of Sheen and
NAPL in Sediment Samples
Petroleum Institute (2, 3).
Section 7 Methods for Performing Shake Testing of Sediment Samples
4.3 Guide E3248 provides guidance regarding when a
Section 8 Categorizing the Relative Presence of NAPL in Sediment
Section 9 Use of NAPL Categorization Results to Select Existing
NAPL movement evaluation is warranted. After confirming
Samples or Identify Locations and Depths for Collecting
that NAPL is present and evaluating nature and extent as
Additional Undisturbed Samples for Laboratory NAPL Mobility
appropriate, the next step in any NAPL movement evaluation Testing
Section 10 Other Methods to Select Samples for Laboratory NAPL Mobility
is to evaluate if NAPL is mobile or immobile at the pore
Testing
scale—this is done using tiered or weight of evidence (WOE)
Section 11 Keywords
approaches. This guide provides a structured process to select
Appendix X1 Recommended Procedure for Visually Characterizing Sediment
for Sheen or NAPL Observations
samples to submit to the laboratory for NAPLmobility testing
Appendix X2 Recommended Procedure for a Sediment-Water Shake Test
that is part of a NAPL movement evaluation.
Appendix X3 Case Study
References
4.4 This guide may be used by various parties involved in
sediment corrective action programs, including regulatory
5. Summary of the Process for Screening and Selection
of Samples for Laboratory NAPL Mobility Testing
5.1 One key factor that typically influences the potential for
Theboldfacenumbersinparenthesesrefertothelistofreferencesattheendof
this standard. NAPL mobility of advectively emplaced NAPL is the NAPL
E3281 − 21a
saturation (that is, the percentage of the total pore space that is 5.2.2 In the second method, whose use depends on site-
filled with NAPL); the distribution of NAPL within the pores specific conditions, the approach is to collect multiple co-
also has an effect on the mobility of the NAPL (that is, a located samples at each sample location during a single
relatively small amount in NAPL within the largest pores can sampling event. With this approach, one core is collected to
produce mobility). Generally, the potential for NAPLmobility determine the nature and extent of NAPL. Additional cores
is greater in sediments containing relatively more NAPL and fromthesamesamplinglocationarearchivedandpreservedin
less in sediments containing relatively less NAPL; for deposi- the original core liners to provide co-located samples for
tionally emplaced NAPLs, the mobility is also strongly influ- subsequent laboratory NAPL mobility testing. Once the rela-
enced by the degree of encapsulation of the NAPL. Therefore, tive amount of NAPL in various areas and depths of sediment
this guide offers a process for qualitatively categorizing the has been characterized, using the methods described in this
relative amount of NAPL present in sediments. This informa- guide, NAPL mobility sampling is performed at targeted
tion is then used to select locations and depth intervals for locations and depths in the archived co-located samples.
laboratory NAPL mobility testing.
5.2.2.1 One advantage of this approach is that laboratory
NAPL mobility test results can be obtained more quickly,
5.2 There are two ways in which the categorization process
because sample material is already available. This approach
presentedinthisguidecanbeusedtoselectlocationsanddepth
generally also has the advantage of being performed in only
intervals for laboratory NAPL mobility testing.
one mobilization.
5.2.1 In the first method, often used in sediment
investigations, grab samples of surface sediment and core 5.2.2.2 The disadvantage of this approach is that it requires
samples of subsurface sediment are collected to determine the collecting co-located samples that can be used for laboratory
natureandextentofNAPL.OncetherelativeamountofNAPL NAPL mobility testing at every sampling station during the
in various areas and depths within the sediment has been initialinvestigationofthenatureandextentofNAPL.Because
categorized using the process described in this guide, NAPL many of the co-located samples would not undergo laboratory
mobility sampling is performed at targeted locations during a testing for NAPL mobility, this approach is less efficient and
subsequent sampling event. can add considerable expense to the investigation program.
5.2.1.1 The advantage of this approach is that previously
5.3 The process for screening and selecting locations and
collected data can be used to select targeted locations and
general depths for laboratory NAPL mobility testing as pre-
general depths for laboratory NAPL mobility testing, so the
sented in this guide consists of the four major steps summa-
subsequent NAPL mobility sampling is focused and efficient.
rized in Fig. 1 and discussed in detail in 5.4. This process is
5.2.1.2 A disadvantage to this approach is that multiple
typicallyperformedinthefield,butthereisnothingprecluding
sampling events are necessary, which could extend the time
the process being applied to sediment samples elsewhere (for
required to complete the site investigation. In some cases,
example, the consultant’s office or at a laboratory).
depending on site-specific conditions (for example, difficult
access, small sampling area) and the number of cores to be 5.4 In this process, sediment samples are screened for the
collected, this approach could be more expensive than the presence of NAPL using a standardized methodology consist-
second method.
ing of visual observations (Step 1) and sediment-water shake
FIG. 1 Summary of the Process for Screening and Selection of Samples for Laboratory NAPL Mobility Testing
E3281 − 21a
testing (Step 2); the relative amount of NAPL is then catego- 5.4.4.3 Differences in mudline elevation and percent recov-
rized in Step 3; finally, decisions regarding the selection of ery should be accounted for when trying to obtain samples
from the same interval in co-located cores. Additionally, the
locations and general depths for laboratory NAPL mobility
tests are made in Step 4. Exact depths of NAPL mobility test sediment lithology should be examined to ensure that it is
comparable for the two intervals from the co-located cores.
samples are usually selected based on detailed photography of
cores collected specifically for NAPL mobility testing.
5.5 The screening process to categorize samples for labora-
5.4.1 Step 1—Avisual observation refers to the appearance
tory NAPL mobility testing provided in this guide offers the
of sheen or NAPL, if present, on and within the sediment
following benefits:
sample. Methods and standard terminology for recording
5.5.1 The use of a standard method for screening sediment
visual observations of sheen and NAPL in sediment samples
samples for the presence of NAPL reduces variability in the
are described in Section 6, and a recommended standardized
reporting of NAPL visual observation data and facilitates
visual observation procedure is provided in Appendix X1.
comparingNAPLpresenceandrelativeabundanceinsediment
across the sediment site. The use of a standard method for
5.4.2 Step 2—A sediment-water shake test is a method for
screening sediment samples for NAPL presence becomes
screening sediments for the presence of NAPL. Aliquots of
particularly important when attempting to compare and inter-
sediment and water are placed in a clear container and gently
pret NAPL observation data collected throughout multiple
shaken; the observation of sheen or NAPL is documented.
investigations or by multiple parties.
Methods for performing shake tests to confirm the presence of
5.5.2 The use of a standard shake test method to comple-
sheen or NAPLin sediment samples and standard terminology
ment visual observations increases the validity of the visual
for recording shake test results are described in Section 7,
observation data and provides a less qualitative measure of the
while a recommended standardized shake test procedure is
relativeamountofNAPLineachshake-testsamplethanvisual
provided in Appendix X2.
observations alone.
5.4.3 Step 3—Visual observations (Step 1) and shake test
5.5.3 Categorizing sediment sampling locations based on
results (Step 2) are compiled to categorize the relative amount
the relative amount of NAPL present in the sediment enables
of NAPL present in each sediment core or grab sample, from
easy identification of areas with relatively more NAPL pres-
least to most NAPL. Sediment cores/grabs are assigned NAPL
ence and relatively less NAPL presence when selecting areas
categories, ranging from Category 1 (no sheen or NAPL
forNAPLmobilitysamplingorexistingsamplesforlaboratory
presentinthesample)throughCategory4(thegreatestrelative
NAPLmobility testing. For sites with more than one sediment
NAPL presence). The process of categorizing the relative
lithologicunit,itispreferablethatthecategorizationresultsfor
presence of NAPL in sediment, based on shake test results, is
allunitsbepooled,ifpossible.However,insomecases,itmay
described in Section 8.
be necessary to separately evaluate categorization results for
5.4.4 Step 4—Based on the results of the NAPLcategoriza-
each lithological unit.
tion (Step 3), locations and general depth intervals are selected
forlaboratoryNAPLmobilitytesting.Thistestingisperformed
6. Methods for Recording Visual Observations of Sheen
eitheroncorescollectedduringasubsequenttargetedsampling
and NAPL in Sediment Samples
program (5.2.1) or from co-located cores that were previously
6.1 This section summarizes methods for systematically
collected and archived in the original core liners (5.2.2). The
describing the visible characteristics of sheen and NAPL in
use of NAPL categories to select locations and general depth
sediment and how to document those observations in a
intervals for laboratory NAPL mobility testing is discussed in
consistent manner using defined terminology.
Section 9.
6.1.1 Thebasicproceduresforvisuallycharacterizingsheen
5.4.4.1 The recommended approach is to evaluate NAPL
andNAPLinsedimentcanbeappliedtosedimentcoreorgrab
mobility across a range of NAPL conditions, with sampling
samples. A detailed methodology for visually characterizing
and testing biased towards locations and depths with relatively
and recording sheen and NAPL observations in sediment is
more NAPL(for example, Category 4), while also performing
included in Appendix X1.
some testing at locations and depths with less NAPL (for
6.1.2 These procedures are performed in addition to stan-
example, Category 3) or even sheen only (that is, Category 2).
dard core logging, which includes (but is not limited to) a
For sites with more than one major sediment lithologic unit,
description of sediment lithology, moisture content, density/
ensure that sufficient representative samples are obtained from
consistency of sediment, and color across the entire length of
each unit.
the core or sample (for guidance see Practices D2487 and
5.4.4.2 The screening process described in this guide re-
D2488).
quires disrupting the sediment matrix, so sediment that has
6.2 Visual observations of sheen and NAPL presence or
been used for visual observation of NAPL presence (for
absence, as well as the distribution of the visual observations
example, the sediment core has been split) or undergone a
within the sediment matrix, can be described using the termi-
shaketestcannotbeusedforNAPLmobilitytesting.Typically,
nology defined in Table 1.
a sediment core collected for NAPL mobility testing would
include up to several meters of intact core material for 6.3 Where sheen is observed in the sediment core or grab
submittal to the laboratory for core photography to select the
sample, the start and end depths for each unique observation
specific depth(s) of the NAPL mobility test sample(s). are recorded, and the sheen color and relative amount of sheen
E3281 − 21a
TABLE 1 Sheen and NAPL Observation Terminology
terminology provided in X1.4. When any aspect of a visual
Standard observationofsheenchanges(forexample,therelativeamount
Appearance
Terminology
observed changes), new start and end depths are recorded.
No visual No sheen or NAPL is observed.
6.3.1 Sheen color can be described using the terminology
evidence of NAPL
provided in Table X1.1, which is modified from Guide F2534.
Sheen A sheen is present, but NAPL is not observed.
6.3.2 The relative amount of sheen observed in the sample
isestimatedbycomparingtherelativesamplesurfaceareawith
Blebs Discrete droplets of NAPL are observed, but for
a sheen to standard comparison charts for visual estimates,
the most part, the sediment matrix is not visibly
contaminated or saturated. Typically, this is such as those provided in Fig. 2 (4) and selecting the
immobile NAPL.
appropriate modifier from Table X1.2.
Coated Sediment grains are coated with NAPL. There is
6.4 Where NAPL is observed in the sediment core or grab
not sufficient NAPL present to saturate the pore
sample, the start and end depths for each unique observation
spaces.
are recorded; the NAPL color, viscosity, and relative amount
Saturated The entirety of the pore space for a sample
are documented using the recommended methods and termi-
appears to be saturated with NAPL. Care should
nology provided in X1.5. When any aspect of a NAPL visual
be taken to ensure that water saturating the pore
observation changes (for example, the relative amount ob-
spaces is not misinterpreted as NAPL when using
this term (for example, use a paper towel to see if
served changes), new start and end depths are recorded.
liquid wicks like water). Depending on the NAPL
6.4.1 Relative NAPL viscosity can be described using the
viscosity, NAPL may freely drain from a sediment
sample. terminology provided in Table X1.4.
6.4.2 Similar to sheen observations, the relative amount of
NAPL observed in the sample is estimated by comparing the
observedaredocumentedusingtherecommendedmethodsand relative sample surface area covered with NAPL to standard
FIG. 2 Visual Estimate Guide
E3281 − 21a
comparison charts for visual estimates, such as those provided Section 6 and Appendix X1. Based on the visual observations,
in Fig. 2, and selecting the appropriate modifier from Table the depth at which to shake test is determined by selecting one
X1.2. or more sampling intervals with the most notable visual
presence of sheen or NAPL using the following sequence (in
6.5 After the visual appearance of sediment is described,
increasing order):
coresandgrabsamplesarephotographedforprojectdocumen-
7.2.1 silverysheen tation and later reference. Section X1.3 provides a standard
NAPL blebs < NAPL coated < NAPL saturated
method for photographing a sediment core; photographs of the
core are taken in 0.3-m to 1.0-m increments (typically, the 7.3 If sheen or NAPL is not observed, select one or more
depth intervals for shake tests based on other criteria, such as
shorter increments are used to provide more detail), with a
scale or tape measure placed next to the core/sample and changes in lithology, sediment discoloration, or elevated pho-
toionization detector (PID) readings. Due to the relatively
included in the photograph to indicate core depth. It is
recommended that photographs be taken straight on, with the small amount of sediment used when performing a shake test,
the shake test should be performed at a specific depth and not
core in the horizontal position and with the shallower depth on
the left and the deeper depth on the right. It is recommended over a wider depth interval.
7.3.1 If visual observations in a sediment core or grab
that sediment cores and grabs are photographed in a well-lit
area with natural light. sample consist of more than one visual observation type (that
is, blebs, coated, saturated, or sheen), the recommended
6.6 For quality control purposes, sheen and NAPL visual
practice is to administer one shake test from a representative
observations,aswellasthestartandenddepthsofthesevisual
sample for each visual observation type in the interval where
observations, should be double-checked for accuracy and
the most notable visual presence of sheen or NAPL for that
consistency by a second trained person.
observation type is observed (that is, one shake test in a sheen
interval with the greatest degree of sheen, one shake test in a
7. Methods for Performing Shake Testing of Sediment
NAPL bleb interval with the greatest degree of NAPL blebs,
Samples
one shake test in a NAPL-coated interval with the greatest
7.1 This section provides an overview of sediment-water
degree of NAPL coating, and one shake test in a NAPL-
shake testing, including methods for selecting sample material
saturatedintervalwiththegreatestdegreeofNAPLsaturation).
to shake test, performing the shake test, and consistently
See X2.3 for additional detailed guidance for determining
documenting the shake test results using defined terminology.
which intervals to perform shake tests on.
A sediment-water shake test is a method for screening sedi-
7.4 To perform a shake test, a consistent ratio of sediment
ments for the presence or absence of NAPL. Aliquots of
and water (see X2.4) is added to a clear container, gently
sediment and water are added to a clear container and shaken,
shaken, and allowed to equilibrate before documenting obser-
then the relative amount of sheen or NAPL is observed.
vations.Forshaketestresultstobecomparable,eachshaketest
7.1.1 Shake testing is considered an effective indicator of
must be performed in the same way using the same type of jar
NAPL presence in a sediment sample, because the NAPL that
(for example, size, shape, material, and lid), the same amounts
may be distributed in the sample, but is not observable, can
of sediment and water, the same intensity and time of shaking,
accumulate as sheens, blebs, or layers (as a direct result of the
and the same amount of time for phase separation after
sediment agitation) after the sediment matrix is disrupted.
shaking. A recommended methodology for shake testing is
While uncommon, if the NAPL present is colorless, adding a
described in detail in Appendix X2.
hydrophobic dye to the sample before the shake test may be
7.5 Todeterminetheshaketestresult,observetheshaketest
necessary.
jar sidewalls and water surface for the presence of sheen,
7.1.2 Although a shake test is a useful indicator of NAPL
NAPL blebs, or a NAPL layer. Describe the shake test results
presence and relative amount, a shake test is not a reliable
using the standard terminology in Table 2. Note that non-
indicatorofNAPLdensity;eitherLNAPLorDNAPLtypically
NAPL material (for example, organic material, ash, miscella-
formsalayerbetweentheairandwaterorcoatsthewallsofthe
neousflocculent)canfloatonthewatersurfaceoradheretothe
sample container because of interfacial tension. Shake tests
sidewalls of the shake test container, potentially confounding
also are not a reliable indicator of NAPL mobility; the
the shake test result.
observed presence of NAPL in a shake test does not provide
any evidence of whether NAPL is mobile at the pore scale in
7.6 When sheen is observed, record the sheen color using
situ.
the terminology for sheen color (Table X1.1) and estimate the
7.1.3 It is possible that shake test results may vary on a
relative amount of sheen present by comparing the relative
site-specific basis. One of the contributing factors to this could
surface area of the water surface covered with a sheen to
be the emplacement mechanism of the NAPL (for example,
standard comparison charts for visual estimates (Fig. 2).
advective versus depositional emplacement).
7.7 When shake test blebs are observed, estimate the rela-
7.1.4 A detailed procedure for conducting sediment-water
tive amount of NAPL present (that is, percent bleb coverage)
shake tests is included in Appendix X2 and summarized in 7.2
by comparing the relative surface area of the jar sidewalls and
through 7.10.
water surface covered with NAPL to standard comparison
7.2 Uponretrievalofasedimentcoreorgrabsample,visual charts for visual estimates (Fig. 2). Also, record the NAPL
observationsofsheenorNAPLaredocumentedasdescribedin color.
E3281 − 21a
TABLE 2 Shake Test Result Terminology
7.10 After the shake test result has been described and
Shake Test Result Appearance photographed, compare visual observations from the represen-
Negative No sheen or NAPL is observed. A negative shake tative sheen or NAPL observation interval to the shake test
test result indicates that sheen and NAPL are not
result. If the shake test result does not corroborate the visual
present in the sample tested.
observationsforthesampledepthinterval,checktheshaketest
Shake test sheen A sheen is present on the surface of the water,
result to confirm that the correct result was recorded. Then,
but no NAPL blebs or NAPL layer is observed. A
review the core interval and ensure that the initial visual
sheen is a silvery, rainbow, or dark rainbow film
observation was correct; update if warranted.
on the surface of water.
7.11 Confirmashaketestwasconductedeachtimeachange
Shake test blebs Discrete droplets of NAPL are present on the
sidewalls of the shake test jar, on the water’s invisualcategorization(asdefinedinTable1)wasobservedin
surface, or suspended in the water.
the sediment core or grab.
Shake test layer NAPL appears as a distinct layer within the shake
7.12 After shake test results have been checked and photo-
test jar, on the water surface. NAPL may also be
graphed and the visual observations for the corresponding
present on the sidewalls of the shake test jar.
depth interval in the sediment sample have been corroborated
against the shake test result, the shake test jar and sediment
sample can be properly discarded. New jars should be used for
subsequent shake tests.
7.8 Whenashaketestlayerisobserved,estimatetheNAPL
7.13 For quality control purposes, conduct one shake test
thickness(ifpossible)andrecordthecolor.Duetothepotential
blank per day using only water to ensure that the shake test
volume of NAPL generated in a shake test with a layer result,
container batch is not biasing results. Field duplicate shake
itmaybedifficulttoseetheNAPLlayer,becausetheshaketest
tests should be performed at a frequency of 5% to 10% of the
jar walls may be covered by NAPL.
shake tests. Field documentation of shake tests should be
7.9 After describing the shake test results, shake tests are
double-checked by a second trained person for accuracy and
photographed for project documentation and later reference
completeness.
(including shake test bleb ranking, if performed, as described
in 8.4). Section X2.5.5 provides a standard method for photo-
8. Categorizing the Relative Presence of NAPL in
graphing the shake test container without the lid from two
Sediment
angles: vertically (that is, from the top, looking down into the
shake test jar at the water surface) and horizontally (that is, 8.1 After completing the screening process described in
from the side, looking at the shake test jar in profile). Sections 6 and 7, shake test results are used to assign a NAPL
Photograph shake tests in a well-lit area, preferably with category for each sampling location (Fig. 3), based on the
natural light.To create a clear contrast between the contents of relative amount of NAPL present (Table 3). The purpose of
the shake test jar and the background, photograph the shake assigningNAPLcategoriesistoreadilyidentifyareasofmore,
test jar on a white surface with a white background. less, or no NAPL presence, to aid in the selection of locations
FIG. 3 Assigning NAPL Categories from Shake Test Results
E3281 − 21a
TABLE 3 NAPL Shake Test Categories
coverage of blebs present in the shake tests and includes a
NAPL Category Criteria check across the entire shake test dataset to confirm consis-
Category 1 Sample locations with negative shake test results, tency in the ranking. Category 3 sample locations with rela-
indicating no sheen or NAPL is present
tively more NAPL presence can then be readily distinguished
from Category 3 sample locations with relatively less NAPL
Category 2 Sample locations with shake test sheen results,
indicating the presence of sheen, but no visible
presence. As shown in Fig. 3, shake test bleb ranking is
NAPL
performed after the field investigation is complete and NAPL
categories have been assigned, so the shake test dataset can be
Category 3 Sample locations with shake test bleb results,
indicating the presence of some visible NAPL evaluated as a whole. The need to further evaluate Category 3
sample locations based on the relative amount of NAPL
Category 4 Sample locations with shake test layer results,
present should be determined on a site-specific basis. The
indicating the presence of relatively more NAPL
shake test bleb ranking process is described in 8.4.1 through
8.5.1.
8.4.1 Shake test bleb ranking will be useful if there are
and depth intervals to collect cores for laboratory NAPL
manyCategory3locationsbutnoCategory4locations(thatis,
mobility testing. These laboratory results can then be used in
shaketestingyieldsmanyshaketestblebsresults,butnoshake
frameworks to determine if the NAPL is mobile at the pore
test layer results) or if the amount of NAPL observed in
scale (see Guide E3282).
Category 3 shake tests varies significantly.
8.2 NAPL categories can be assigned on a core or grab 8.4.2 To perform shake test bleb ranking, at least two (but
sample location basis, based on the specific lithology type (for preferablythree)trainedpersonnelshouldreviewtheshaketest
example,recentdepositsvs.glacialtill),toaspecificdepth(for photographs, shake test field logs, and the sediment core or
example, surface sediment vs. subsurface sediment), or based grab sample logs for Category 3 locations to estimate the
on any other site-specific metric.
percent coverage of blebs present on the shake test water
surface and adhered to the jar walls (that is, percent bleb
8.3 In the example described in this section, NAPL catego-
coverage) to the nearest 5%. This is done using standard
ries are assigned based on the shake test result containing the
comparison charts for visual estimates, such as those provided
greatest relative amount of NAPL for a given core or grab
in Fig. 2.
sample location, so that the NAPL category represents the
8.4.2.1 Thepercentblebcoveragerecorded,whentheshake
greatest relative amount of NAPL at any depth at a given
test results were logged (see 7.6), can be used for one of the
location. When assigning a NAPL category, select the shake
three estimates.
test with the greatest relative amount of NAPL using the
8.4.2.2 When reviewing shake test photographs, note that
following sequence (in increasing order):
water in shake tests can range in appearance from clear to
8.3.1 negative shake test < shake test sheen < shake test
darkly colored or opaque, due to the composition of the shake
blebs (all ranks) < shake test layer
tested sediment (for example, organic silt, clay, sand). Organic
8.3.1.1 The NAPL categories, from least to greatest NAPL
and anthropogenic material in sediment can appear as solids
presence, are assigned as summarized in Fig. 3 and described
floating on the water in the shake test jar or adhered to shake
in Table 3.
test jar walls. Therefore, shake test photographs should be
8.3.2 Given that the relative amount of NAPL present in a
interpreted taking into consideration the sediment type, visual
shake test jar with blebs can vary significantly, Category 3
observationsofsheenorNAPLinthesedimentsampleandthe
cores/grabs can be further evaluated based on the degree of
shake test results documented on the shake test field logs.
NAPL accumulation in the shake test jar (that is, shake test
bleb ranking), from least to most NAPL. The shake test bleb 8.4.3 If all the bleb coverage estimates by the trained
ranking process is described in 8.4. personnel are within 20%, use the highest estimate to assign
8.3.3 For example, consider a core with visual observations theblebrank.Iftheblebcoverageestimatesvarybymorethan
ofnone,sheen,andNAPLsaturatedatdifferentdepthintervals, 20%, the reviewers should re-evaluate the shake test photo-
with corresponding shake test results of negative, sheen, and graphs and field information to develop consensus on the bleb
layer, respectively. The visual observation containing the coverage estimate. The consensus bleb coverage estimate is
greatest relative amount of NAPL for this core is NAPL then used to assign the shake test bleb rank.
saturated. The shake test result containing the greatest relative
8.4.4 Beforefinalizingtheshaketestblebranks,thefollow-
amountofNAPLforthiscoreistheshaketestlayer,whichwas
ing quality assurance measures should be taken to establish
associated with the NAPL saturated visual observation. The
consistency in rank estimates across the entire shake test
NAPL category for this core would be assigned based on the
dataset:
shake test layer result, which would result in this core being
8.4.4.1 Compileandcompareshaketestphotographswithin
assigned to Category 4.
each bleb rank for consistency.
8.4.4.2 Compile and compare shake test photographs be-
8.4 Depending on site-specific conditions, shake test bleb
tween bleb ranks to confirm that increasing bleb ranks consis-
rankingisrecommendedtofurtherevaluateCategory3sample
tently reflect increasing quantities of bleb coverage.
locations, based on the relative amount of NAPL present.
Shake test bleb ranking consists of using estimates of the 8.4.5 See the case study (Appendix X3) for an example of
percent bleb coverage in the shake test jar to rank the percent shake test bleb ranking.
E3281 − 21a
8.5 Depending on site-specific conditions or program 9.2.2.1 IfdifferenttypesofNAPL(thatis,differentphysical
objectives, it may be useful to develop a relationship between or chemical characteristics) are observed, sampling locations
visual observations and shake test results, to infer the relative should provide spatial coverage of each.
NAPLquantity in intervals that were not shake tested and had
9.2.3 ThemajorityofNAPLmobilitytestsamplesshouldbe
only visual observations made on them.
collected from locations where cores were collected and
8.5.1 The relationship between visual observations and
processedforbothvisualobservationsandshaketests,because
shaketestresultsshouldbeassessedonasite-specificbasis,by
the results will enable a comparison between the NAPL
reviewing the results of the visual observation and shake test
categories assigned using this guide and NAPL mobility test
screening data to confirm the presence of a consistent relation-
results.
ship.Anexampleofthesite-specificrelationshipbetweenthese
9.2.4 The screening process described in this guide requires
two screening methods is presented in the case study (Appen-
disturbingthesedimentmatrix,sothesedimentsamplethathas
dix X3).
been used for visual observations and shake testing is not
suitable for NAPL mobility testing. Typically, an intact co-
9. Use of NAPL Categorization Results to Select Existing
located sediment core collected for NAPL mobility testing
Samples or Identify Locations and Depths for
would be retained in the original core liner and would include
Collecting Additional Undisturbed Samples for
up to several meters of core material. The core would be cut
Laboratory NAPL Mobility Testing
into increments suitable for shipping and submitted to the
laboratoryforcorephotographytoselectthespecificdepthsfor
9.1 The results of the NAPL categorization discussed in
the NAPL mobility test samples.
Section8canbeusedtoselectlocationsanddepthintervalsfor
collection of undisturbed samples in a subsequent sampling
9.3 Appendix X3 presents a case study illustrating the
program, or to choose existing samples for laboratory NAPL
application of this selection process and a NAPL mobility
mobility testing; this testing will evaluate if NAPL present in
investigation and evaluation designed using the approach
the sediment sample is mobile or immobile at the pore scale.
outlined in this guide.
Objectives for laboratory NAPL mobility testing will vary
based on site-specific conditions and data needs. However, the
10. Other Methods to Select Samples for Laboratory
approach for characterizing the amount of NAPL in a sample
NAPL Mobility Testing
(which provides some indication of the potential for NAPL
10.1 Each of the technologies described in this section can
mobility) in this guide is general, suitable for a range of sites,
be used to identify NAPL presence, and the magnitude of
and adaptable to site-specific conditions and data needs.
response can be used to interpret relative amount of NAPL in
9.2 As noted in Section 5, NAPL saturation (that is, the
sediment. In general, locations and depths with the greatest
percentage of the total pore space that is filled with NAPL)
relative amount of NAPL should be preferentially targeted for
influences the potential for NAPL mobility via advection in
NAPL mobility testing.Additional NAPL mobility testing can
sediment.Generally,thepotentialforNAPLmobilityisgreater
be performed at locations and depths with less NAPLpresence
in sediments with relatively more NAPLand less in sediments
to provide NAPL mobility test results across a range of
withrelativelylessNAPL;indepositionallyemplacedNAPLs,
conditions.
the mobility is also strongly influenced by the degree of
10.2 Ultraviolet (UV) Light Screening:
encapsulation of the NAPL. Therefore, the recommended
10.2.1 Petroleum hydrocarbon, creosote, and coal tar
approach is to collect more samples for laboratory NAPL
mobility testing at locations and depths where screening has NAPLs are partially composed of individual polycyclic aro-
matic hydrocarbons (PAHs) of varying concentrations. PAHs
indicatedahigherpotentialformobileNAPL(thatis,locations
and depths with relatively more NAPL, such as Category 4 will generally fluoresce under excitation by UV light. The
intensityofthefluorescenceresponsemayprovideaqualitative
locations) and fewer samples at locations and depths with
lesser amounts of NAPL (that is, such as Category 3 and indication of the relative magnitude of NAPL in a sample but
can also vary depending upon other factors, including grain
Category 2 locations), where NAPL is more likely immobile.
Recommendations on designing a NAPL mobility sampling sizeandNAPLtype.Thecoloroffluorescencemayprovidean
indication of PAH composition (PAH mixtures principally
program to achieve these objectives are provided in 9.2.1
through 9.2.3. composed of two aromatic rings will generally appear blue
shifted, whereas mixtures principally composed of five aro-
9.2.1 It is recommended that NAPL mobility sampling
locations be biased towards areas or depths with a higher matic rings will generally appear red shifted) (5).
potential for NAPL mobility. 10.2.2 Because NAPLcan be difficult to visually identify in
9.2.2 NAPL mobility sampling locations should also pro- dark-colored sediments, field or laboratory screening of a
vide spatial coverage across areas with a higher potential for sediment core with UV light can provide useful information
mobile NAPL (for example, Category 4 areas, and if bleb regarding the presence, distribution, and primary composition
ranking is
...


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: E3281 − 21 E3281 − 21a
Standard Guide for
NAPL Mobility and Migration in Sediments – Screening
Process to Categorize Samples for Laboratory NAPL
Mobility Testing
This standard is issued under the fixed designation E3281; 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 is designed for general application at a wide range of sediment sites where non-aqueous phase liquid (NAPL) is
present or suspected to be present in the sediment. This guide describes a process to use field screening methods, specifically visual
observations, and the results of shake tests, to categorize the relative amount of NAPL present in a sample. This categorization can
then be utilized to select co-located sediment samples for laboratory testing to determine if the NAPL in the sample interval is
mobile or immobile at the pore scale, or any other chemical or physical testing.
1.1.1 There is no current industry standard methodology to select sediment samples for laboratory NAPL mobility testing; the use
of different methodologies is possible. This guide focuses on a selection process that uses visual observations and shake tests. This
process has the advantage of being simple to use and, if applied in a disciplined manner, has been demonstrated to provide good
results in the field.
1.2 This guide is intended to inform, complement, and support characterization and remedial efforts performed under international,
federal, state, and local environmental programs but not supersede local, state, federal, or international regulations. The users of
this guide should review existing information and data available for a sediment site to determine applicable regulatory agency
requirements and the most appropriate entry point into and use of this guide.
1.3 ASTM International (ASTM) standard guides are not regulations; they are consensus standard guides that may be followed
voluntarily to support applicable regulatory requirements. This guide may be used in conjunction with other ASTM guides
developed for assessing sediment sites.
1.4 This guide does not address methods and means of sample collection (Guide E3163).
1.5 Units—The values stated in SI or CGS units are to be regarded as the 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.
This guide is under the jurisdiction of ASTM Committee E50 on Environmental Assessment, Risk Management and Corrective Action and is the direct responsibility
of Subcommittee E50.04 on Corrective Action.
Current edition approved April 1, 2021Oct. 1, 2021. Published June 2021November 2021. Originally approved in 2021. Last previous edition approved in 2021 as
E3281–21. DOI: 10.1520/E3281–2110.1520/E3281–21A
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
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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.
2. Referenced Documents
2.1 ASTM Standards:
D2487 Practice for Classification of Soils for Engineering Purposes (Unified Soil Classification System)
D2488 Practice for Description and Identification of Soils (Visual-Manual Procedures)
D7203 Practice for Screening Trichloroethylene (TCE)-Contaminated Media Using a Heated Diode Sensor
E2531 Guide for Development of Conceptual Site Models and Remediation Strategies for Light Nonaqueous-Phase Liquids
Released to the Subsurface
E2856 Guide for Estimation of LNAPL Transmissivity
E3163 Guide for Selection and Application of Analytical Methods and Procedures Used during Sediment Corrective Action
E3248 Guide for NAPL Mobility and Migration in Sediment – Conceptual Models for Emplacement and Advection
E3268 Guide for NAPL Mobility and Migration in Sediment—Sample Collection, Field Screening, and Sample Handling
E3282 Guide for NAPL Mobility and Migration in Sediments – Evaluation Metrics
F2534 Guide for Visually Estimating Oil Spill Thickness on Water
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 Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
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3. Terminology
3.1 Definitions:
3.1.1 immobile NAPL, n—NAPL that does not move by advection within the connected void spaces of the sediment under
specified physical and chemical conditions, as may be demonstrated by laboratory testing, or may be interpreted based on
mathematical calculations or modeling. E3248
3.1.2 mobile NAPL, n—NAPL that may move by advection within the connected void spaces of the sediment under specific
physical and chemical conditions, as may be demonstrated by laboratory testing, or as may be interpreted based on mathematical
calculations or modeling. E3248
3.1.3 non-aqueous phase liquid, NAPL, n—chemicals that are insoluble or only slightly soluble in water that exist as a separate
liquid phase in environmental media. E3248
3.1.3.1 Discussion—
NAPL may be less dense than water (light non-aqueous phase liquid [LNAPL]) or more dense than water (dense non-aqueous
phase liquid [DNAPL]).
3.1.4 pore scale, n—the scale of the connected void spaces within the sediment. E3248
3.1.5 sediment(s), n—a matrix of pore water and particles including gravel, sand, silt, clay, and other natural and anthropogenic
substances that have settled at the bottom of a tidal or nontidal body of water. E3163
3.1.6 sheen, n—a silvery, rainbow, or dark rainbow film on the surface of the sediment sample or on a water surface.
4. Significance and Use
4.1 NAPLs (for example, chlorinated solvents, petroleum products, and creosote) can be emplaced in sediments through a variety
of mechanisms (Guide E3248). Dense non-aqueous phase liquids (DNAPLs) are more dense than water, whereas light non-aqueous
phase liquids (LNAPLs) are less dense than water.
4.2 Standardized guidance and test methods currently exist for assessing NAPL mobility at upland sites, from organizations such
as ASTM (Guides E2531 and E2856), Interstate Technology & Regulatory Council (1) and the American Petroleum Institute (2,
3).
4.3 Guide E3248 provides guidance regarding when a NAPL movement evaluation is warranted. After confirming that NAPL is
present and evaluating nature and extent as appropriate, the next step in any NAPL movement evaluation is to evaluate if NAPL
is mobile or immobile at the pore scale—this is done using tiered or weight of evidence (WOE) approaches. This guide provides
a structured process to select samples to submit to the laboratory for NAPL mobility testing that is part of a NAPL movement
evaluation.
4.4 This guide may be used by various parties involved in sediment corrective action programs, including regulatory agencies,
project sponsors, environmental consultants, toxicologists, risk assessors, site remediation professionals, environmental
contractors, and other stakeholders.
4.5 This guide should be used in conjunction with other reference material (refer to Section 2 and References) that direct the user
in developing and implementing sediment assessment programs.
4.6 This guide is related to Guide E3163, concerning sediment analytical techniques used during sediment programs. It is related
This relates to Guide E3248, which discusses generic models for the emplacement and advection of NAPL in sediments. It is
related to Guide E3268, which describes sample collection, field screening and sample handling considerations in NAPL
movement evaluations. And this is related to Guide E3282, which describes evaluation metrics and frameworks to determine if
NAPL is immobile or immobile at the pore scale, or if it is migrating or stable at the NAPL body scale.
The boldface numbers in parentheses refer to the list of references at the end of this standard.
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4.7 This guide does not replace the need for engaging competent persons to evaluate NAPL emplacement and movement in
sediments. Activities necessary to develop a conceptual site model should be conducted by persons familiar with NAPL-impacted
sediment site characterization techniques, physical and chemical properties of NAPL in sediments, fate and transport processes,
remediation technologies, and sediment evaluation protocols. The users of this guide should consider assembling a team of
experienced project professionals with appropriate expertise to scope, plan, and execute sediment NAPL data acquisition activities.
4.8 This guide provides a framework based on overarching features and elements that should be customized by the user, based
on site-specific conditions, regulatory context, and program objectives for a particular sediment site. This guide should not be used
alone as a prescriptive checklist.
4.9 The user of this guide should review the overall structure and components of this guide before proceeding with use, including:
Section 1 Scope
Section 2 Referenced Documents
Section 3 Terminology
Section 4 Significance and Use
Section 5 Summary of the Process for Screening and Selection of Samples for Laboratory NAPL Mobility Testing
Section 6 Methods for Recording Visual Observations of Sheen and NAPL in Sediment Samples
Section 7 Methods for Performing Shake Testing of Sediment Samples
Section 8 Categorizing the Relative Presence of NAPL in Sediment
Section 9 Use of NAPL Categorization Results to Select Existing Samples or Identify Locations and Depths for Collecting Additional
Undisturbed Samples for Laboratory NAPL Mobility Testing
Section 10 Other Methods to Select Samples for Laboratory NAPL Mobility Testing
Section 11 Keywords
Appendix X1 Recommended Procedure for Visually Characterizing Sediment for Sheen or NAPL Observations
Appendix X2 Recommended Procedure for a Sediment-Water Shake Test
Appendix X3 Case Study
References
5. Summary of the Process for Screening and Selection of Samples for Laboratory NAPL Mobility Testing
5.1 One key factor that typically influences the potential for NAPL mobility of advectively emplaced NAPL is the NAPL
saturation (that is, the percentage of the total pore space that is filled with NAPL); the distribution of NAPL within the pores also
has an effect on the mobility of the NAPL (that is, a relatively small amount in NAPL within the largest pores can produce
mobility). Generally, the potential for NAPL mobility is greater in sediments containing relatively more NAPL and less in
sediments containing relatively less NAPL; for depositionally emplaced NAPLs, the mobility is also strongly influenced by the
degree of encapsulation of the NAPL. Therefore, this guide offers a process for qualitatively categorizing the relative amount of
NAPL present in sediments. This information is then used to select locations and depth intervals for laboratory NAPL mobility
testing.
5.2 There are two ways in which the categorization process presented in this guide can be used to select locations and depth
intervals for laboratory NAPL mobility testing.
5.2.1 In the first method, often used in sediment investigations, grab samples of surface sediment and core samples of subsurface
sediment are collected to determine the nature and extent of NAPL. Once the relative amount of NAPL in various areas and depths
within the sediment has been categorized using the process described in this guide, NAPL mobility sampling is performed at
targeted locations during a subsequent sampling event.
5.2.1.1 The advantage of this approach is that previously collected data can be used to select targeted locations and general depths
for laboratory NAPL mobility testing, so the subsequent NAPL mobility sampling is focused and efficient.
5.2.1.2 A disadvantage to this approach is that multiple sampling events are necessary, which could extend the time required to
complete the site investigation. In some cases, depending on site-specific conditions (for example, difficult access, small sampling
area) and the number of cores to be collected, this approach could be more expensive than the second method.
5.2.2 In the second method, whose use depends on site-specific conditions, the approach is to collect multiple co-located samples
at each sample location during a single sampling event. With this approach, one core is collected to determine the nature and extent
of NAPL. Additional cores from the same sampling location are archived and preserved in the original core liners to provide
co-located samples for subsequent laboratory NAPL mobility testing. Once the relative amount of NAPL in various areas and
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depths of sediment has been characterized, using the methods described in this guide, NAPL mobility sampling is performed at
targeted locations and depths in the archived co-located samples.
5.2.2.1 One advantage of this approach is that laboratory NAPL mobility test results can be obtained more quickly, because sample
material is already available. This approach generally also has the advantage of being performed in only one mobilization.
5.2.2.2 The disadvantage of this approach is that it requires collecting co-located samples that can be used for laboratory NAPL
mobility testing at every sampling station during the initial investigation of the nature and extent of NAPL. Because many of the
co-located samples would not undergo laboratory testing for NAPL mobility, this approach is less efficient and can add
considerable expense to the investigation program.
5.3 The process for screening and selecting locations and general depths for laboratory NAPL mobility testing as presented in this
guide consists of the four major steps summarized in Fig. 1 and discussed in detail in 5.4. This process is typically performed in
the field, but there is nothing precluding the process being applied to sediment samples elsewhere (for example, the consultant’s
office or at a laboratory).
5.4 In this process, sediment samples are screened for the presence of NAPL using a standardized methodology consisting of
visual observations (Step 1) and sediment-water shake testing (Step 2); the relative amount of NAPL is then categorized in Step
3; finally, decisions regarding the selection of locations and general depths for laboratory NAPL mobility tests are made in Step
4. Exact depths of NAPL mobility test samples are usually selected based on detailed photography of cores collected specifically
for NAPL mobility testing.
5.4.1 Step 1—A visual observation refers to the appearance of sheen or NAPL, if present, on and within the sediment sample.
Methods and standard terminology for recording visual observations of sheen and NAPL in sediment samples are described in
Section 6, and a recommended standardized visual observation procedure is provided in Appendix X1.
5.4.2 Step 2—A sediment-water shake test is a method for screening sediments for the presence of NAPL. Aliquots of sediment
and water are placed in a clear container and gently shaken; the observation of sheen or NAPL is documented. Methods for
performing shake tests to confirm the presence of sheen or NAPL in sediment samples and standard terminology for recording
shake test results are described in Section 7, andwhile a recommended standardized shake test procedure is provided in Appendix
X2.
5.4.3 Step 3—Visual observations (Step 1) and shake test results (Step 2) are compiled to categorize the relative amount of NAPL
present in each sediment core or grab sample, from least to most NAPL. Sediment cores/grabs are assigned NAPL categories,
ranging from Category 1 (no sheen or NAPL present in the sample) through Category 4 (the greatest relative NAPL presence). The
process of categorizing the relative presence of NAPL in sediment, based on shake test results, is described in Section 8.
FIG. 1 Summary of the Process for Screening and Selection of Samples for Laboratory NAPL Mobility Testing
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5.4.4 Step 4—Based on the results of the NAPL categorization (Step 3), locations and general depth intervals are selected for
laboratory NAPL mobility testing. This testing is performed either on cores collected during a subsequent targeted sampling
program (5.2.1) or from co-located cores that were previously collected and archived in the original core liners (5.2.2). The use
of NAPL categories to select locations and general depth intervals for laboratory NAPL mobility testing is discussed in Section
9.
5.4.4.1 The recommended approach is to evaluate NAPL mobility across a range of NAPL conditions, with sampling and testing
biased towards locations and depths with relatively more NAPL (for example, Category 4), while also performing some testing
at locations and depths with less NAPL (for example, Category 3) or even sheen only (that is, Category 2). For sites with more
than one major sediment lithologic unit, ensure that sufficient representative samples are obtained from each unit.
5.4.4.2 The screening process described in this guide requires disrupting the sediment matrix, so sediment that has been used for
visual observation of NAPL presence (for example, the sediment core has been split) or undergone a shake test cannot be used for
NAPL mobility testing. Typically, a sediment core collected for NAPL mobility testing would include up to several meters of intact
core material for submittal to the laboratory for core photography to select the specific depth(s) of the NAPL mobility test
sample(s).
5.4.4.3 Differences in mudline elevation and percent recovery should be accounted for when trying to obtain samples from the
same interval in co-located cores. Additionally, the sediment lithology should be examined to ensure that it is comparable for the
two intervals from the co-located cores.
5.5 The screening process to categorize samples for laboratory NAPL mobility testing provided in this guide offers the following
benefits:
5.5.1 The use of a standard method for screening sediment samples for the presence of NAPL reduces variability in the reporting
of NAPL visual observation data and facilitates comparing NAPL presence and relative abundance in sediment across the sediment
site. The use of a standard method for screening sediment samples for NAPL presence becomes particularly important when
attempting to compare and interpret NAPL observation data collected throughout multiple investigations or by multiple parties.
5.5.2 The use of a standard shake test method to complement visual observations increases the validity of the visual observation
data and provides a less qualitative measure of the relative amount of NAPL in each shake-test sample than visual observations
alone.
5.5.3 Categorizing sediment sampling locations based on the relative amount of NAPL present in the sediment enables easy
identification of areas with relatively more NAPL presence and relatively less NAPL presence when selecting areas for NAPL
mobility sampling or existing samples for laboratory NAPL mobility testing. For sites with more than one sediment lithologic unit,
it is preferable that the categorization results for all units be pooled, if possible. However, in some cases, it may be necessary to
separately evaluate categorization results for each lithological unit.
6. Methods for Recording Visual Observations of Sheen and NAPL in Sediment Samples
6.1 This section summarizes methods for systematically describing the visible characteristics of sheen and NAPL in sediment and
how to document those observations in a consistent manner using defined terminology.
6.1.1 The basic procedures for visually characterizing sheen and NAPL in sediment can be applied to sediment core or grab
samples. A detailed methodology for visually characterizing and recording sheen and NAPL observations in sediment is included
in Appendix X1.
6.1.2 These procedures are performed in addition to standard core logging, which includes (but is not limited to) a description of
sediment lithology, moisture content, density/consistency of sediment, and color across the entire length of the core or sample (for
guidance see Practices D2487 and D2488).
6.2 Visual observations of sheen and NAPL presence or absence, as well as the distribution of the visual observations within the
sediment matrix, can be described using the terminology defined in Table 1.
6.3 Where sheen is observed in the sediment core or grab sample, the start and end depths for each unique observation are
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TABLE 1 Sheen and NAPL Observation Terminology
Standard
Appearance
Terminology
No visual No sheen or NAPL is observed.
evidence of NAPL
Sheen A sheen is present, but NAPL is not observed.
Blebs Discrete droplets of NAPL are observed, but for
the most part, the sediment matrix is not visibly
contaminated or saturated. Typically, this is
immobile NAPL.
Coated Sediment grains are coated with NAPL. There is
not sufficient NAPL present to saturate the pore
spaces.
Saturated The entirety of the pore space for a sample
appears to be saturated with NAPL. Care should
be taken to ensure that water saturating the pore
spaces is not misinterpreted as NAPL when using
this term (for example, use a paper towel to see if
liquid wicks like water). Depending on the NAPL
viscosity, NAPL may freely drain from a sediment
sample.
recorded, and the sheen color and relative amount of sheen observed are documented using the recommended methods and
terminology provided in X1.4. When any aspect of a visual observation of sheen changes (for example, the relative amount
observed changes), new start and end depths are recorded.
6.3.1 Sheen color can be described using the terminology provided in Table X1.1, which is modified from Guide F2534.
6.3.2 The relative amount of sheen observed in the sample is estimated by comparing the relative sample surface area with a sheen
to standard comparison charts for visual estimates, such as those provided in Fig. 2 (4) and selecting the appropriate modifier from
Table X1.2.
6.4 Where NAPL is observed in the sediment core or grab sample, the start and end depths for each unique observation are
recorded; the NAPL color, viscosity, and relative amount are documented using the recommended methods and terminology
provided in X1.5. When any aspect of a NAPL visual observation changes (for example, the relative amount observed changes),
new start and end depths are recorded.
6.4.1 Relative NAPL viscosity can be described using the terminology provided in Table X1.4.
6.4.2 Similar to sheen observations, the relative amount of NAPL observed in the sample is estimated by comparing the relative
sample surface area covered with NAPL to standard comparison charts for visual estimates, such as those provided in Fig. 2, and
selecting the appropriate modifier from Table X1.2.
6.5 After the visual appearance of sediment is described, cores and grab samples are photographed for project documentation and
later reference. Section X1.3 provides a standard method for photographing a sediment core; photographs of the core are taken in
0.3-m to 1.0-m increments (typically, the shorter increments are used to provide more detail), with a scale or tape measure placed
next to the core/sample and included in the photograph to indicate core depth. It is recommended that photographs be taken straight
on, with the core in the horizontal position and with the shallower depth on the left and the deeper depth on the right. It is
recommended that sediment cores and grabs are photographed in a well-lit area with natural light.
6.6 For quality control purposes, sheen and NAPL visual observations, as well as the start and end depths of these visual
observations, should be double-checked for accuracy and consistency by a second trained person.
7. Methods for Performing Shake Testing of Sediment Samples
7.1 This section provides an overview of sediment-water shake testing, including methods for selecting sample material to shake
test, performing the shake test, and consistently documenting the shake test results using defined terminology. A sediment-water
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FIG. 2 Visual Estimate Guide
shake test is a method for screening sediments for the presence or absence of NAPL. Aliquots of sediment and water are added
to a clear container and shaken, then the relative amount of sheen or NAPL is observed.
7.1.1 Shake testing is considered an effective indicator of NAPL presence in a sediment sample, because the NAPL that may be
distributed in the sample, but is not observable, can accumulate as sheens, blebs, or layers (as a direct result of the sediment
agitation) after the sediment matrix is disrupted. While uncommon, if the NAPL present is colorless, adding a hydrophobic dye
to the sample before the shake test may be necessary.
7.1.2 Although a shake test is a useful indicator of NAPL presence and relative amount, a shake test is not a reliable indicator of
NAPL density; either LNAPL or DNAPL typically forms a layer between the air and water or coats the walls of the sample
container because of interfacial tension. Shake tests also are not a reliable indicator of NAPL mobility; the observed presence of
NAPL in a shake test does not provide any evidence of whether NAPL is mobile at the pore scale in situ.
7.1.3 It is possible that shake test results may vary on a site-specific basis. One of the contributing factors to this could be the
emplacement mechanism of the NAPL (for example, advective versus depositional emplacement).
7.1.4 A detailed procedure for conducting sediment-water shake tests is included in Appendix X2 and summarized in 7.2 through
7.10.
7.2 Upon retrieval of a sediment core or grab sample, visual observations of sheen or NAPL are documented as described in
Section 6 and Appendix X1. Based on the visual observations, the depth at which to shake test is determined by selecting one or
more sampling intervals with the most notable visual presence of sheen or NAPL using the following sequence (in increasing
order):
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7.2.1 silvery sheen < rainbow sheen < dark rainbow sheen < NAPL blebs < NAPL coated < NAPL saturated
7.3 If sheen or NAPL is not observed, select one or more depth intervals for shake tests based on other criteria, such as changes
in lithology, sediment discoloration, or elevated photoionization detector (PID) readings. Due to the relatively small amount of
sediment used when performing a shake test, the shake test should be performed at a specific depth and not over a wider depth
interval.
7.3.1 If visual observations in a sediment core or grab sample consist of more than one visual observation type (that is, blebs,
coated, saturated, or sheen), the recommended practice is to administer one shake test from a representative sample for each visual
observation type in the interval where the most notable visual presence of sheen or NAPL for that observation type is observed
(that is, one shake test in a sheen interval with the greatest degree of sheen, one shake test in a NAPL bleb interval with the greatest
degree of NAPL blebs, one shake test in a NAPL-coated interval with the greatest degree of NAPL coating, and one shake test
in a NAPL-saturated interval with the greatest degree of NAPL saturation). See X2.3 for additional detailed guidance for
determining which intervals to perform shake tests on.
7.4 To perform a shake test, a consistent ratio of sediment and water (see X2.4) areis added to a clear container, gently shaken,
and allowed to equilibrate before documenting observations. For shake test results to be comparable, each shake test must be
performed in the same way using the same type of jar (for example, size, shape, material, and lid), the same amounts of sediment
and water, the same intensity and time of shaking, and the same amount of time for phase separation after shaking. A recommended
methodology for shake testing is described in detail in Appendix X2.
7.5 To determine the shake test result, observe the shake test jar sidewalls and water surface for the presence of sheen, NAPL
blebs, or a NAPL layer. Describe the shake test results using the standard terminology in Table 2. Note that non-NAPL material
(for example, organic material, ash, miscellaneous flocculent) can float on the water surface or adhere to the sidewalls of the shake
test container, potentially confounding the shake test result.
7.6 When sheen is observed, record the sheen color using the terminology for sheen color (Table X1.1) and estimate the relative
amount of sheen present by comparing the relative surface area of the water surface covered with a sheen to standard comparison
charts for visual estimates (Fig. 2).
7.7 When shake test blebs are observed, estimate the relative amount of NAPL present (that is, percent bleb coverage) by
comparing the relative surface area of the jar sidewalls and water surface covered with NAPL to standard comparison charts for
visual estimates (Fig. 2). Also, record the NAPL color.
7.8 When a shake test layer is observed, estimate the NAPL thickness (if possible) and record the color. Due to the potential
volume of NAPL generated in a shake test with a layer result, it may be difficult to see the NAPL layer, because the shake test
jar walls may be covered by NAPL.
7.9 After describing the shake test results, shake tests are photographed for project documentation and later reference (including
TABLE 2 Shake Test Result Terminology
Shake Test Result Appearance
Negative No sheen or NAPL is observed. A negative shake
test result indicates that sheen and NAPL are not
present in the sample tested.
Shake test sheen A sheen is present on the surface of the water,
but no NAPL blebs or NAPL layer is observed. A
sheen is a silvery, rainbow, or dark rainbow film
on the surface of water.
Shake test blebs Discrete droplets of NAPL are present on the
sidewalls of the shake test jar, on the water’s
surface, or suspended in the water.
Shake test layer NAPL appears as a distinct layer within the shake
test jar, on the water surface. NAPL may also be
present on the sidewalls of the shake test jar.
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shake test bleb ranking, if performed, as described in 8.4). Section X2.5.5 provides a standard method for photographing the shake
test container without the lid from two angles: vertically (that is, from the top, looking down into the shake test jar at the water
surface) and horizontally (that is, from the side, looking at the shake test jar in profile). Photograph shake tests in a well-lit area,
preferably with natural light. To create a clear contrast between the contents of the shake test jar and the background, photograph
the shake test jar on a white surface with a white background.
7.10 After the shake test result has been described and photographed, compare visual observations from the representative sheen
or NAPL observation interval to the shake test result. If the shake test result does not corroborate the visual observations for the
sample depth interval, check the shake test result to confirm that the correct result was recorded. Then, review the core interval
and ensure that the initial visual observation was correct; update if warranted.
7.11 Confirm a shake test was conducted each time a change in visual categorization (as defined in Table 1) was observed in the
sediment core or grab.
7.12 After shake test results have been checked and photographed and the visual observations for the corresponding depth interval
in the sediment sample have been corroborated against the shake test result, the shake test jar and sediment sample can be properly
discarded. New jars should be used for subsequent shake tests.
7.13 For quality control purposes, conduct one shake test blank per day using only water to ensure that the shake test container
batch is not biasing results. Field duplicate shake tests should be performed at a frequency of 5 % to 10 % of the shake tests. Field
documentation of shake tests should be double-checked by a second trained person for accuracy and completeness.
8. Categorizing the Relative Presence of NAPL in Sediment
8.1 After completing the screening process described in Sections 6 and 7, shake test results are used to assign a NAPL category
for each sampling location (Fig. 3), based on the relative amount of NAPL present (Table 3). The purpose of assigning NAPL
categories is to readily identify areas of more, less, or no NAPL presence, to aid in the selection of locations and depth intervals
to collect cores for laboratory NAPL mobility testing. These laboratory results can then be used in frameworks to determine if the
NAPL is mobile at the pore scale (see Guide E3282).
8.2 NAPL categories can be assigned on a core or grab sample location basis, based on the specific lithology type (for example,
recent deposits vs. glacial till), to a specific depth (for example, surface sediment vs. subsurface sediment), or based on any other
site-specific metric.
FIG. 3 Assigning NAPL Categories from Shake Test Results
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TABLE 3 NAPL Shake Test Categories
NAPL Category Criteria
Category 1 Sample locations with negative shake test results,
indicating no sheen or NAPL is present
Category 2 Sample locations with shake test sheen results,
indicating the presence of sheen, but no visible
NAPL
Category 3 Sample locations with shake test bleb results,
indicating the presence of some visible NAPL
Category 4 Sample locations with shake test layer results,
indicating the presence of relatively more NAPL
8.3 In the example described in this section, NAPL categories are assigned based on the shake test result containing the greatest
relative amount of NAPL for a given core or grab sample location, so that the NAPL category represents the greatest relative
amount of NAPL at any depth at a given location. When assigning a NAPL category, select the shake test with the greatest relative
amount of NAPL using the following sequence (in increasing order):
8.3.1 negative shake test < shake test sheen < shake test blebs (all ranks) < shake test layer
8.3.1.1 The NAPL categories, from least to greatest NAPL presence, are assigned as summarized in Fig. 3 and described in Table
3.
8.3.2 Given that the relative amount of NAPL present in a shake test jar with blebs can vary significantly, Category 3 cores/grabs
can be further evaluated based on the degree of NAPL accumulation in the shake test jar (that is, shake test bleb ranking), from
least to most NAPL. The shake test bleb ranking process is described in 8.4.
8.3.3 For example, consider a core with visual observations of none, sheen, and NAPL saturated at different depth intervals, with
corresponding shake test results of negative, sheen, and layer, respectively. The visual observation containing the greatest relative
amount of NAPL for this core is NAPL saturated. The shake test result containing the greatest relative amount of NAPL for this
core is the shake test layer, which was associated with the NAPL saturated visual observation. The NAPL category for this core
would be assigned based on the shake test layer result, which would result in this core being assigned to Category 4.
8.4 Depending on site-specific conditions, shake test bleb ranking is recommended to further evaluate Category 3 sample
locations, based on the relative amount of NAPL present. Shake test bleb ranking consists of using estimates of the percent bleb
coverage in the shake test jar to rank the percent coverage of blebs present in the shake tests and includes a check across the entire
shake test dataset to confirm consistency in the ranking. Category 3 sample locations with relatively more NAPL presence can then
be readily distinguished from Category 3 sample locations with relatively less NAPL presence. As shown in Fig. 3, shake test bleb
ranking is performed after the field investigation is complete and NAPL categories have been assigned, so the shake test dataset
can be evaluated as a whole. The need to further evaluate Category 3 sample locations based on the relative amount of NAPL
present should be determined on a site-specific basis. The shake test bleb ranking process is described in 8.4.1 through 8.5.1.
8.4.1 Shake test bleb ranking will be useful if there are many Category 3 locations but no Category 4 locations (that is, shake
testing yields many shake test blebs results, but no shake test layer results) or if the amount of NAPL observed in Category 3 shake
tests varies significantly.
8.4.2 To perform shake test bleb ranking, at least two (but preferably three) trained personnel should review the shake test
photographs, shake test field logs, and the sediment core or grab sample logs for Category 3 locations to estimate the percent
coverage of blebs present on the shake test water surface and adhered to the jar walls (that is, percent bleb coverage) to the nearest
5 %. This is done using standard comparison charts for visual estimates, such as those provided in Fig. 2.
8.4.2.1 The percent bleb coverage recorded, when the shake test results were logged (see 7.6), can be used for one of the three
estimates.
8.4.2.2 When reviewing shake test photographs, note that water in shake tests can range in appearance from clear to darkly colored
or opaque, due to the composition of the shake tested sediment (for example, organic silt, clay, sand). Organic and anthropogenic
material in sediment can appear as solids floating on the water in the shake test jar or adhered to shake test jar walls. Therefore,
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shake test photographs should be interpreted taking into consideration the sediment type, visual observations of sheen or NAPL
in the sediment sample and the shake test results documented on the shake test field logs.
8.4.3 If all the bleb coverage estimates by the trained personnel are within 20 %, use the highest estimate to assign the bleb rank.
If the bleb coverage estimates vary by more than 20 %, the reviewers should re-evaluate the shake test photographs and field
information to develop consensus on the bleb coverage estimate. The consensus bleb coverage estimate is then used to assign the
shake test bleb rank.
8.4.4 Before finalizing the shake test bleb ranks, the following quality assurance measures should be taken to establish consistency
in rank estimates across the entire shake test dataset:
8.4.4.1 Compile and compare shake test photographs within each bleb rank for consistency.
8.4.4.2 Compile and compare shake test photographs between bleb ranks to confirm that increasing bleb ranks consistently reflect
increasing quantities of bleb coverage.
8.4.5 See the case study (Appendix X3) for an example of shake test bleb ranking.
8.5 Depending on site-specific conditions or program objectives, it may be useful to develop a relationship between visual
observations and shake test results, to infer the relative NAPL quantity in intervals that were not shake tested and had only visual
observations made on them.
8.5.1 The relationship between visual observations and shake test results should be assessed on a site-specific basis, by reviewing
the results of the visual observation and shake test screening data to confirm the presence of a consistent relationship. An example
of the site-specific relationship between these two screening methods is presented in the case study (Appendix X3).
9. Use of NAPL Categorization Results to Select Existing Samples or Identify Locations and Depths for Collecting
Additional Undisturbed Samples for Laboratory NAPL Mobility Testing
9.1 The results of the NAPL categorization discussed in Section 8 can be used to select locations and depth intervals for collection
of undisturbed samples in a subsequent sampling program, or to choose existing samples for laboratory NAPL mobility testing;
this testing will evaluate if NAPL present in the sediment sample is mobile or immobile at the pore scale. Objectives for laboratory
NAPL mobility testing will vary based on site-specific conditions and data needs. However, the approach for characterizing the
amount of NAPL in a sample (which provides some indication of the potential for NAPL mobility) in this guide is general, suitable
for a range of sites, and adaptable to site-specific conditions and data needs.
9.2 As noted in Section 5, NAPL saturation (that is, the percentage of the total pore space that is filled with NAPL) influences
the potential for NAPL mobility via advection in sediment. Generally, the potential for NAPL mobility is greater in sediments with
relatively more NAPL and less in sediments with relatively less NAPL; in depositionally emplaced NAPLs, the mobility is also
strongly influenced by the degree of encapsulation of the NAPL. Therefore, the recommended approach is to collect more samples
for laboratory NAPL mobility testing at locations and depths where screening has indicated a higher potential for mobile NAPL
(that is, locations and depths with relatively more NAPL, such as Category 4 locations) and fewer samples at locations and depths
with lesser amounts of NAPL (that is, such as Category 3 and Category 2 locations), where NAPL is more likely immobile.
Recommendations on designing a NAPL mobility sampling program to achieve these objectives are provided in 9.2.1 through
9.2.3.
9.2.1 It is recommended that NAPL mobility sampling locations be biased towards areas or depths with a higher potential for
NAPL mobility.
9.2.2 NAPL mobility sampling locations should also provide spatial coverage across areas with a higher potential for mobile
NAPL (for example, Category 4 areas, and if bleb ranking is performed, Category 3 areas with greater than 50 % bleb coverage)
and areas with lesser amounts of NAPL where NAPL is likely immobile (for example, Category 3 areas; if bleb ranking is
performed, Category 3 areas with less than 50 % bleb coverage; Category 2 areas).
9.2.2.1 If different types of NAPL (that is, different physical or chemical characteristics) are observed, sampling locations should
provide spatial coverage of each.
9.2.3 The majority of NAPL mobility test samples should be collected from locations where cores were collected and processed
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for both visual observations and shake tests, because the results will enable a comparison between the NAPL categories assigned
using this guide and NAPL mobility test results.
9.2.4 The screening process described in this guide requires disturbing the sediment matrix, so the sediment sample that has been
used for visual observations and shake testing is not suitable for NAPL mobility testing. Typically, an intact co-located sediment
core collected for NAPL mobility testing would be retained in the original core liner and would include up to several meters of
core material. The core would be cut into increments suitable for shipping and submitted to the laboratory for core photography
to select the specific depths for the NAPL mobility test samples.
9.3 Appendix X3 presents a case study illustrating the application of this selection process and a NAPL mobility investigation and
evaluation designed using the approach outlined in this guide.
10. Other Methods to Select Samples for Laboratory NAPL Mobility Testing
10.1 Each of the technologies described in this section can be used to identify NAPL presence, and the magnitude of response can
be used to interpret relative
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