Standard Practice for Decontamination of Field Equipment Used at Nonradioactive Waste Sites

SIGNIFICANCE AND USE
An appropriately developed, executed and documented equipment decontamination procedure is an integral and essential part of waste site investigations. The benefits of its use include:
5.1.1 Minimizing the spread of contaminants within a study area and from site to site,
5.1.2 Reducing the potential for worker exposure by means of contact with contaminated sampling equipment, and
5.1.3 Improved data quality and reliability.
This practice is not a substitute for a well-documented Quality Assurance/Quality Control (QA/QC) program. Because the ultimate test of a decontamination procedure is its ability to minimize erroneous data, a reasonable QA/QC program must be implemented.
This practice may not be applicable to all waste sites. When a sampling effort is completed to determine only the general range of chemical concentrations of interest less rigorous decontamination procedures can be adequate. Investigators should have the flexibility to modify the decontamination procedures with due consideration for the sampling objective or if QA/QC documentation supports alternative decontamination methods.
At sites where the reactivity of sampling equipment to decontamination washes creates concern for the generation of undesirable chemical by-products, the use of dedicated sampling equipment should be considered.
This practice, where applicable, should be used before, between, and after the completion of sampling events.
These practices are appropriate for use at sites where chemical (organic and inorganic) contamination is known or expected. The application of these practices to other types of sites radiological, mixed (radiological and chemical), or biohazard contaminated sites may not be applicable. The application of these practices to these types of sites should be undertaken with care and consideration, along with QA/QC documentation that supports the effectiveness of these decontamination techniques.
SCOPE
1.1 This practice covers the decontamination of field equipment used in the sampling of soils, soil gas, sludges, surface water, and ground water at waste sites which are to undergo both physical and chemical analyses.
1.2 These practices are applicable only at sites where chemical (organic and inorganic) wastes are a concern. It is not intended for use at radiological, mixed (chemical and radiological), or biohazard sites.
1.3 Procedures are included for the decontamination of equipment which comes into contact with the sample matrix (sample contacting equipment) and for ancillary equipment that has not contacted the portion of sample to be analyzed (non-sample contacting equipment).
1.4 These practices are based on commonly recognized methods by which equipment may be decontaminated. The procedures described for sample contacting equipment are commonly prescribed, however there is a minimum of scientific data that supports these methods (Mickam et al. 1989, Parker, 1995). Therefore the user is reminded of the importance of QA/QC samples that document decontamination effectiveness and that these samples can be used to modify or enhance decontamination techniques. Decontamination at radiologically contaminated sites should refer to Practice D 5608.
1.5 This practice is applicable to most conventional sampling equipment constructed of metallic and synthetic materials. The manufacturer of a specific sampling apparatus should be contacted if there is concern regarding the reactivity of a decontamination rinsing agent with the equipment.
1.6 This practice 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 judgement. Not all aspects of this practice 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 profe...

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09-Jan-2002
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ASTM D5088-02 - Standard Practice for Decontamination of Field Equipment Used at Nonradioactive Waste Sites
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NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.
Contact ASTM International (www.astm.org) for the latest information
Designation:D5088–02
Standard Practices for
1
Decontamination of Field Equipment Used at Waste Sites
This standard is issued under the fixed designation D 5088; 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* course of action. This document cannot replace education or
experience and should be used in conjunction with professional
1.1 This practice covers the decontamination of field equip-
judgement. Not all aspects of this practice may be applicable in
ment used in the sampling of soils, soil gas, sludges, surface
all circumstances. This ASTM standard is not intended to
water, and ground water at waste sites which are to undergo
represent or replace the standard of care by which the
both physical and chemical analyses.
adequacy of a given professional service must be judged, nor
1.2 These practices are applicable only at sites where
should this document be applied without consideration of a
chemical (organic and inorganic) wastes are a concern. It is not
project’s many unique aspects. The word “Standard” in the
intended for use at radiological, mixed (chemical and radio-
title of this document means only that the documents has been
logical), or biohazard sites.
approved through the ASTM consensus process.
1.3 Procedures are included for the decontamination of
1.7 This standard does not purport to address the safety
equipment which comes into contact with the sample matrix
problems associated with its use. It is the responsibility of the
(sample contacting equipment) and for ancillary equipment
user of this standard to establish appropriate safety and health
that has not contacted the portion of sample to be analyzed
practices and determine the applicability of regulatory limita-
(non-sample contacting equipment).
tions prior to use.
1.4 These practices are based on commonly recognized
methods by which equipment may be decontaminated. The
2. Referenced Documents
procedures described for sample contacting equipment are
2.1 ASTM Standards:
commonly prescribed, however there is a minimum of scien-
2 D 653 Terminology Relating to Soil, Rock, and Contained
tific data that supports these methods (Mickam et al. 1989 ,
5
34
Fluids
Parker , 1995). Therefore the user is reminded of the impor-
D 5608 Practice for Decontamination of Field Equipment
tance of QA/QC samples that document decontamination
5
Used at Low Level Radioactive Waste Sites
effectiveness and that these samples can be used to modify or
enhance decontamination techniques. Decontamination at ra-
3. Terminology
diologically contaminated sites should refer to Practice
3.1 Definitions:
D 5608.
3.1.1 contaminant—an undesirable substance not normally
1.5 This practice is applicable to most conventional sam-
present or an unusually high concentration of a naturally
pling equipment constructed of metallic and synthetic materi-
occurring substance in water or soil.
als. The manufacturer of a specific sampling apparatus should
3.1.2 control rinse water—water used for equipment wash-
be contacted if there is concern regarding the reactivity of a
ing and rinsing having a known chemistry.
decontamination rinsing agent with the equipment.
3.1.3 decontamination—the process of removing or reduc-
1.6 This practice offers an organized collection of informa-
ing to a known level undesirable physical or chemical constitu-
tion or a series of options and does not recommend a specific
ents, or both, from a sampling apparatus to maximize the
representativeness of physical or chemical analyses proposed
1
This practice is under the jurisdiction of ASTM Committee D18 on Soil and
for a given sample.
Rock and is the direct responsibility of Subcommittee D18.21 on GroundWater and
3.1.4 non-sample contacting equipment—related equipment
Vadose Zone Investigations.
associated with the sampling effort, but that does not directly
Current edition approved Jan. 10, 2002. Published April 2002. Originally
published as D 5088–90. Last previous edition D 5088–90.
contact the sample (for example, augers, drilling rods, excava-
2
Mickam, J.T., R. Bellandi, and E.C. Tifft, Jr., 1989, Equipment Decontamina-
tions machinery).
tion Procedures for Ground Water and Vadose Zone Monitoring Programs: Status
3.1.5 quality assurance/quality control (QA/QC)—the ef-
and Prospects, Ground Water Monitoring Review 9, No 2:100–121.
3
forts completed to evaluate the accuracy and precision of a
Parker, L.V., 1996A Literature Review on Decontaminating Groundwater
Sampling Devices: Organic Contaminates.CRREL Report 95–14, U.S. Army Cold
sampling or testing procedure, or both.
Regions Research and
...

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