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ASTM D5633-04

(Practice)

Standard Practice for Sampling with a Scoop

Standard Practice for Sampling with a Scoop

SIGNIFICANCE AND USE
This practice is intended for use in collecting samples of contaminated soils and similar materials.
Scoops are used primarily for collecting samples near the surface. Subsurface samples can be obtained by first removing higher layers using a shovel or other suitable equipment and collecting the sample with the scoop.
Because of their simplicity, scoops are useful in taking samples of waste materials where decontamination or disposal is a problem with other types of sampling equipment. Scoops are also suitable for use in rapid screening programs, pilot studies, and other semi-quantitative investigations.
Samples should be collected in accordance with an appropriate work plan (see Practice D 5283 and Guide D 4687).
SCOPE
1.1 This procedure covers the method and equipment used to collect surface and near-surface samples of soils and physically similar materials using a scoop.  
1.2  This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.

General Information

Status
Historical
Publication Date
31-Mar-2004
ICS
13.080.05 - Examination of soils in general
Technical Committee
D34 - Waste Management
Drafting Committee
D34.01.03 - Sampling Equipment
Current Stage
Ref Project

Relations

Replaces
ASTM D5633-94(2001) - Standard Practice for Sampling with a Scoop
Effective Date
01-Apr-2004
Replaced By
ASTM D5633-04(2008) - Standard Practice for Sampling with a Scoop
Effective Date
01-Sep-2008
Referred By
ASTM D5658-20 - Standard Practice for Sampling Unconsolidated Waste from Trucks
Effective Date
01-Apr-2004
Referred By
ASTM E1963-22 - Standard Guide for Conducting Terrestrial Plant Toxicity Tests
Effective Date
01-Apr-2004
Referred By
ASTM D6232-21 - Standard Guide for Selection of Sampling Equipment for Waste and Contaminated Media Data Collection Activities
Effective Date
01-Apr-2004
Referred By
ASTM D5680-14(2022) - Standard Practice for Sampling Unconsolidated Solids in Drums or Similar Containers
Effective Date
01-Apr-2004
Referred By
ASTM D7204-15 - Standard Practice for Sampling Waste Streams on Conveyors
Effective Date
01-Apr-2004

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ASTM D5633-04 - Standard Practice for Sampling with a ScoopASTM D5633-04 - Standard Practice for Sampling with a Scoop
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ASTM D5633-04 - Standard Practice for Sampling with a Scoop
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Standards Content (Sample)

NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.
Contact ASTM International (www.astm.org) for the latest information
Designation:D5633–04
Standard Practice for
1
Sampling with a Scoop
This standard is issued under the fixed designation D 5633; 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 (e) indicates an editorial change since the last revision or reapproval.
1. Scope ment. A clean scoop is then used to collect the actual sample,
which is placed in a sample container.
1.1 This procedure covers the method and equipment used
to collect surface and near-surface samples of soils and
4. Significance and Use
physically similar materials using a scoop.
4.1 This practice is intended for use in collecting samples of
1.2 This standard does not purport to address all of the
contaminated soils and similar materials.
safety concerns, if any, associated with its use. It is the
4.2 Scoops are used primarily for collecting samples near
responsibility of the user of this standard to establish appro-
the surface. Subsurface samples can be obtained by first
priate safety and health practices and determine the applica-
removing higher layers using a shovel or other suitable
bility of regulatory limitations prior to use.
equipment and collecting the sample with the scoop.
2. Referenced Documents 4.3 Because of their simplicity, scoops are useful in taking
2
samples of waste materials where decontamination or disposal
2.1 ASTM Standards:
is a problem with other types of sampling equipment. Scoops
D 4687 Guide for General Planning of Waste Sampling
are also suitable for use in rapid screening programs, pilot
D 5088 Practice for Decontamination of Field Equipment
studies, and other semi-quantitative investigations.
Used at Nonradioactive Waste Sites
4.4 Samples should be collected in accordance with an
D 5283 Practice for Generation of Environmental Data
appropriate work plan (see Practice D 5283 and Guide
Related to Waste Management Activities: Quality Assur-
D 4687).
ance and Quality Control Planning and Implementation
D 5792 Practice for Generation of Environmental Data
5. Sampling Equipment
Related to Waste ManagementActivities: Development of
5.1 Ashovel or other suitable equipment can be used for the
Data Quality Objectives
initial removal of overburden material. This equipment should
D 6044 Guide for Representative Sampling for Manage-
be manufactured from material that is compatible with the soil
ment of Waste and Contaminated Media
or waste to be sampled. The scoop must be manufactured from
D 6232 Guide for Selection of Sampling Equipment for
material that is compatible with the soil or waste to be sampled
Waste and Contaminated Media Data CollectionActivities
and the required test or analysis to be performed. For most
2.2 Other Documents:
hazardous waste sampling, either a disposable plastic scoop or
Pierre Gy’s Sampling Theory and Sampling Practice, Fran-
3 a reusable stainless steel or polytetrafluoroethylene-coated
cis F. Pitard
scoop is suitable (see Guide 6232 and Practice 5792).
3. Summary of Practice 5.2 The design of the scoop is important to minimize
sampling error, that is, all the material intended as the sample
3.1 The top layers of material are removed down to the
can be collected and placed in the sample container and is not
required sample depth using a shovel or other suitable equip-
lost as the scoop is systematically lifted from the source to the
sample container (see Guide D 6044, Pierre Gy’s Sampling
1
This practice is under the jurisdiction of ASTM Committee D34 on Waste
Theory and Sampling Practice and Fig. 1).
Management and is the direct responsibility of Subcommittee D34.01.03 on Sample
5.3 For measurement of sample depth, a ruler or tape
Preservation.
measure can be used.
Current edition approved April 1, 2004. Published May 2004. Originally
approved in 1994. Last previous edition approved in 1994 as D 5633-94(2001).
5.4 The advantages of sampling with a scoop are that the
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
scoops are:
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
5.4.1 inexpensive,
Standards volume information, refer to the standard’s Document Summary page on
5.4.2 easy to use, and
the ASTM website.
3
Available from CRC Press, Inc., 2000 Corporate Blvd., NW, Boca Raton, FL
5.4.3 easy to clean.
33431.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1

---------------------- Page: 1 ----------------------
D5633–04
7.2 Use a shovel or other suitable equipment to remove any
overburden material down to the level specified in the work
plan.
7.3 Measure to the depth at which the sample will be
collected with a ruler or tape measure. Record th
...

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ASTM D6907-22(Practice)
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5.1 Bucket augers (Fig. 1) are relatively inexpensive, readily available, available in different types depending on the media to be sampled, and most can be easily operated by one person. They collect a reasonably cylindrical but disturbed sample of surface or subsurface soil or waste. They are generally not suited for sampling gravelly or coarser soil and are unsuitable for sampling rock. There are other designs of hand augers, such as the Edelman auger, used to retrieve difficult materials such as waste, sands, peat, and mud.
FIG. 1 Bucket Auger  
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1.1 This practice describes the procedures and equipment used to collect surface and subsurface soil and contaminated media samples for chemical analysis using a hand-operated bucket auger (sometimes referred to as a barrel auger). Several types of bucket augers exist and are designed for sampling various types of soil. All bucket augers collect disturbed samples. Bucket augers can also be used to auger to the desired sampling depth and then, using a core-type sampler, collect a relatively undisturbed sample suitable for chemical analysis.  
1.2 This practice does not cover the use of large 300 mm or greater diameter bucket augers mechanically operated by large drill rigs or similar equipment, such as those described in Practice D1452/D1452M, paragraph 5.2.4. Practice D1452/D1452M on auger borings refers to this hand auger included in Practice D6907 as a barrel auger.  
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SIGNIFICANCE AND USE
5.1 This practice is intended for use in collecting samples of contaminated soils and similar materials.  
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SIGNIFICANCE AND USE
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4.4 Since natural ...
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1.2 The guide is focused on hydrocarbon chemicals of concern (COCs) that include petroleum hydrocarbons derived from crude oil (for example, motor fuels, jet oils, lubricants, petroleum solvents, and used oils) and other hydrocarbon NAPLs (for example, creosote and coal tars). While much of what is discussed may be relevant to other organic chemicals, the applicability of the standard to other NAPLs, like chlorinated solvents or polychlorinated biphenyls (PCBs), is not included in this guide.  
1.3 This guide is intended to evaluate the role of NAPL natural attenuation towards reaching the remedial objectives and/or performance goals at a specific site; and the selection of an appropriate remedy, including remediation through monitoring of natural or enhanced attenuation, or the remedy transition to natural mechanisms. While the evaluation can support some aspects of site characterization, the development of the conceptual site model and risk assessment, it is not intended to replace risk assessment and mitigation, such as addressing potential impact to human health or environment, or need for source control.  
1.4 Estimation of NAPL natural attenuation rates in the subsurface relies on indirect measurements of environmental indicators and their variation in time and space. Available methods described in this standard are based on evaluation of biogeochemical reactions and physical transport processes combined with data analysis to infer and quantify the natural attenuation rates for NAPL present in the vadose and/or saturated zones.  
1.5...

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ASTM
ASTM D7521-22(Test Method)
Standard Test Method for Determination of Asbestos in Soil

SIGNIFICANCE AND USE
5.1 This analysis method is used for the testing of soil samples for asbestos. The emphasis is on detection and analysis of sieved particles for asbestos in the soil. Debris identifiable as bulk building material that is readily separable from the soil is to be analyzed and reported separately.  
5.2 The coarse fraction of the sample (>2 mm to  
5.3 This test method does not describe procedures or techniques required to evaluate the safety or habitability of buildings or outdoor areas potentially contaminated with asbestos-containing materials or compliance with federal, state, or local regulations or statutes. It is the investigator's responsibility to make these determinations.  
5.4 Whereas this test method produces results that may be used for evaluation of sites contaminated by construction, mine, and manufacturing wastes; deposits of natural occurrences of asbestos; and other sources of interest to the investigator, the application of the results to such evaluations and the conclusions drawn there from, including any assessment of risk or liability, is beyond the scope of this test method and is the responsibility of the investigator.
SCOPE
1.1 This test method covers a procedure to: (1) identify asbestos in soil, (2) provide an estimate of the concentration of asbestos in the sampled soil (dried), and (3) optionally to provide a concentration of asbestos reported as the number of asbestos structures per gram of sample.  
1.2 In this test method, results are produced that may be used for evaluation of sites contaminated by construction, mine and manufacturing wastes, deposits of natural occurrences of asbestos (NOA), and other sources of interest to the investigator.  
1.3 This test method describes the gravimetric, sieve, and other laboratory procedures for preparing the soil for analysis as well as the identification and quantification of any asbestos detected. Pieces of collected soil and material embedded therein that pass through a 19-mm sieve will become part of the sample that is analyzed and for which results are reported.  
1.3.1 Asbestos is identified and quantified by polarized light microscopy (PLM) techniques including analysis of morphology and optical properties. Optional transmission electron microscopy (TEM) identification and quantification of asbestos is based on morphology, selected area electron diffraction (SAED), and energy dispersive X-ray analysis (EDXA). Some information about fiber size may also be determined. The PLM and TEM methods use different definitions and size criteria for fibers and structures. Separate data sets may be produced.  
1.4 This test method has an analytical sensitivity of 0.25 % by weight with optional procedures to allow for an analytical sensitivity of 0.1 % by weight.  
1.5 This test method does not purport to address sampling strategies or variables associated with soil environments. Such considerations are the responsibility of the investigator collecting and submitting the sample. Appendix X2 covering elements of soil sampling and good field practices is attached.  
1.6 Units—The values stated in SI units are to be regarded as the standard. Other units may be cited in the method for informational purposes only.  
1.7 Hazards—Asbestos fibers are acknowledged carcinogens. Breathing asbestos fibers can result in disease of the lungs including asbestosis, lung cancer, and mesothelioma. Precautions should be taken to avoid creating and breathing airborne asbestos particles when sampling and analyzing materials suspected of containing asbestos.  
1.8 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.9 This international standard was developed in accordance with internationally ...

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ASTM
ASTM D7014-22(Practice)
Standard Practice for Installation of Double-Twisted Wire Mesh Gabions and Revet Mattresses

SIGNIFICANCE AND USE
4.1 Gabions and Revet Mattresses, as described in Specification A975, are used to achieve soil stability and prevent soil erosion and are also used as retaining wall structures to resist movements due to gravity. Their ability to function properly depends on correct design and installation. This standard practice describes the proper installation of gabions and revet mattresses to ensure the products function as intended by the manufacturers.
SCOPE
1.1 This specification covers standard practice for foundation preparation, assembly, placement and filling of double-twisted wire mesh gabions and revet mattresses used for various erosion control, soil retention or freestanding structures.  
1.2 This guide offers an organized collection of information or a series of options and does not recommend a specific course of action. This document cannot replace education or experience and should be used in conjunction with professional judgment. Not all aspects of this guide may be applicable in all circumstances. This ASTM standard is not intended to represent or replace the standard of care by which the adequacy of a given professional service must be judged, nor should this document be applied without consideration of a project’s many unique aspects. The word “Standard” in the title of this document means only that the document has been approved through the ASTM consensus process."  
1.3 Units—The values stated in SI units are to be regarded as standard. The values given in parentheses are provided for information only and are not considered standard.  
1.4 This standard may involve hazardous materials, operations, and equipment. This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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