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ASTM F2532-13

(Guide)

Standard Guide for Determining Net Environmental Benefit of Dispersant Use

Standard Guide for Determining Net Environmental Benefit of Dispersant Use

SIGNIFICANCE AND USE
3.1 Net Environmental Benefit Analysis (NEBA) when applied to oil spill response, is the process of considering advantages and disadvantages of different spill response options (including a no response baseline) and comparing them to identify a spill response decision resulting in the lowest overall environmental and socioeconomic impacts from an oil spill and the response to that spill.  
3.2 Spill response will likely involve some combination of response options. There are no response methods that are completely effective or risk-free. NEBA should be conducted with appropriate regulatory agencies and other organizations as part of spill response contingency planning. NEBA is important for pre-spill planning since some response options have a limited window of opportunity.
SCOPE
1.1 This guide covers considerations in assessing net environmental benefit of dispersant use on oil spills. The purpose of this guide is to minimize environmental and socioeconomic impacts of oil spills.  
1.2 Net environmental benefit analysis (NEBA) of all response options should be conducted as part of oil spill contingency planning.  
1.3 There are many methods to control or cleanup oil spills. All spill response options should be given equal consideration.  
1.4 Only general guidance is provided here. It is assumed that the crude or fuel oil is dispersible. The dispersant is assumed to be relatively effective, applied correctly, and in compliance with relevant government regulations. Differences between commercial dispersants or between different oils are not considered in this guide.  
1.5 This guide applies to marine and estuarine environments only.  
1.6 When making dispersant use decisions, appropriate government authorities should be consulted as required by law.  
1.7 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.

General Information

Status
Historical
Publication Date
30-Nov-2013
ICS
13.020.40 - Pollution, pollution control and conservation
Technical Committee
F20 - Hazardous Substances and Oil Spill Response
Drafting Committee
F20.13 - Treatment
Current Stage
Ref Project

Relations

Replaces
ASTM F2532-06 - Standard Guide for Determining Net Environmental Benefit of Dispersant Use
Effective Date
01-Dec-2013
Replaced By
ASTM F2532-19 - Standard Guide for Determining Net Environmental Benefit of Dispersant Use
Effective Date
01-Mar-2019
Referred By
ASTM F1210-19 - Standard Guide for Ecological Considerations for the Use of Oil Spill Dispersants in Freshwater and Other Inland Environments, Lakes and Large Water Bodies
Effective Date
01-Dec-2013
Referred By
ASTM F1737/F1737M-23 - Standard Guide for Use of Oil Spill Dispersant Application Equipment During Spill Response: Boom and Nozzle Systems
Effective Date
01-Dec-2013
Referred By
ASTM F1231-19 - Standard Guide for Ecological Considerations for the Use of Oil Spill Dispersants in Freshwater and Other Inland Environments, Rivers and Creeks
Effective Date
01-Dec-2013
Referred By
ASTM F2204/F2204M-22 - Standard Guide for Describing Shoreline and Inland Response Techniques
Effective Date
01-Dec-2013
Referred By
ASTM F1872-21 - Standard Guide for Use of Chemical Shoreline Cleaning Agents: Environmental and Operational Considerations
Effective Date
01-Dec-2013
Referred By
ASTM F2205-22 - Standard Guide for Ecological Considerations for the Use of Chemical Dispersants in Oil Spill Response: Tropical Environments
Effective Date
01-Dec-2013
Referred By
ASTM F1209-19 - Standard Guide for Ecological Considerations for the Use of Oil Spill Dispersants in Freshwater and Other Inland Environments, Ponds and Sloughs
Effective Date
01-Dec-2013

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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:F2532 −13
Standard Guide for
1
Determining Net Environmental Benefit of Dispersant Use
This standard is issued under the fixed designation F2532; 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 3. Significance and Use
1.1 This guide covers considerations in assessing net envi- 3.1 Net Environmental Benefit Analysis (NEBA) when
ronmentalbenefitofdispersantuseonoilspills.Thepurposeof applied to oil spill response, is the process of considering
this guide is to minimize environmental and socioeconomic advantages and disadvantages of different spill response op-
impacts of oil spills. tions(includinganoresponsebaseline)andcomparingthemto
identify a spill response decision resulting in the lowest overall
1.2 Net environmental benefit analysis (NEBA) of all re-
environmentalandsocioeconomicimpactsfromanoilspilland
sponse options should be conducted as part of oil spill
the response to that spill.
contingency planning.
3.2 Spill response will likely involve some combination of
1.3 There are many methods to control or cleanup oil spills.
response options. There are no response methods that are
All spill response options should be given equal consideration.
completely effective or risk-free. NEBA should be conducted
1.4 Only general guidance is provided here. It is assumed
withappropriateregulatoryagenciesandotherorganizationsas
that the crude or fuel oil is dispersible. The dispersant is
part of spill response contingency planning. NEBA is impor-
assumed to be relatively effective, applied correctly, and in
tant for pre-spill planning since some response options have a
compliance with relevant government regulations. Differences
limited window of opportunity.
between commercial dispersants or between different oils are
not considered in this guide.
4. Net Environmental Benefit Analysis for Oil Spill
Response
1.5 Thisguideappliestomarineandestuarineenvironments
only.
4.1 The objective of NEBA is to choose the oil spill
response option that will result in the lowest overall negative
1.6 When making dispersant use decisions, appropriate
impact on the environment. The NEBA should focus on local
government authorities should be consulted as required by law.
and regional areas of concern and should result in decisions
1.7 This standard does not purport to address all of the
based on what is best for a specific location. With NEBA
safety concerns, if any, associated with its use. It is the
comes the recognition that, regardless of the response option
responsibility of the user of this standard to establish appro-
chosen, some impact will occur. Table 1 and Table 2 and
priate safety and health practices and determine the applica-
Appendix X1 and Appendix X4 provide considerations for use
bility of regulatory limitations prior to use.
in the NEBAprocess. Appendix X2 and Appendix X3 present
2. Referenced Documents
an ecological risk assessment method for determining the net
2
environmental benefit of dispersant use.
2.1 ASTM Standards:
3
F1788 Guide for In-Situ Burning of Oil Spills on Water:
4.2 The NEBA process involves several tasks (1, 2).
Environmental and Operational Considerations
4.2.1 Gatherinformationonhabitatsandspeciesofconcern,
F2205 Guide for Ecological Considerations for the Use of
physical and chemical characteristics of the spilled oil, shore-
Chemical Dispersants in Oil Spill Response: Tropical
line geomorphology, potential socioeconomic impacts, and
Environments
spill response options. Resource trustees, area contingency
plans, and environmental sensitivity maps are good sources of
1
This guide is under the jurisdiction of ASTM Committee F20 on Hazardous
information.
Substances and Oil Spill Response and is the direct responsibility of Subcommittee
4.2.2 Consider the relative importance of natural resources
F20.13 on Treatment.
and their vulnerability and sensitivity to oiling in the region
Current edition approved Dec. 1, 2013. Published January 2014. Originally
approved in 2006. Last previous edition approved in 2006 as F2532–06. DOI: and time period of interest.
10.1520/F2532-13.
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
3
Standards volume information, refer to the standard’s Document Summary page on The boldface numbers in parentheses refer to the list of references at the end of
the ASTM website. this standard.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 --------------
...

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: F2532 − 06 F2532 − 13
Standard Guide for
1
Determining Net Environmental Benefit of Dispersant Use
This standard is issued under the fixed designation F2532; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope
1.1 This guide covers considerations in determiningassessing net environmental benefit of dispersant use on oil spills. The
purpose of this guide is to minimize environmental and socioeconomic impacts of oil spills.
1.2 Net environmental benefit analysis (NEBA) of all response options should be conducted as part of oil spill contingency
planning.
1.3 There are many methods to control or cleanup oil spills. Dispersants All spill response options should be given equal
consideration with other spill response options.consideration.
1.4 Only general guidance is provided here. It is assumed that the crude or fuel oil is dispersible. The dispersant is assumed to
be relatively effective, applied correctly, and in compliance with relevant government regulations. Differences between commercial
dispersants or between different oils are not considered in this guide.
1.5 This guide applies to marine and estuarine environments only.
1.6 When making dispersant use decisions, appropriate government authorities should be consulted as required by law.
1.7 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory
limitations prior to use.
2. Referenced Documents
2
2.1 ASTM Standards:
F1788 Guide for In-Situ Burning of Oil Spills on Water: Environmental and Operational Considerations
F2205 Guide for Ecological Considerations for the Use of Chemical Dispersants in Oil Spill Response: Tropical Environments
3. Significance and Use
3.1 Net Environmental Benefit Analysis (NEBA) when applied to oil spill response, is the process of considering advantages
and disadvantages of different spill response options (including no response) to arrive at a no response baseline) and comparing
them to identify a spill response decision resulting in the lowest overall environmental and socioeconomic impacts.impacts from
an oil spill and the response to that spill.
3.2 Spill response will likely involve some combination of response options. There are no response methods that are completely
effective or risk-free. NEBA should be conducted with appropriate regulatory agencies and other organizations as part of spill
response contingency planning. NEBA is important for pre-spill planning since some response options have a limited window of
opportunity.
4. Net Environmental Benefit Analysis for Oil Spill Response
4.1 The objective of NEBA is to choose the oil spill response option that will result in the lowest overall negative impact on
the environment. The NEBA should focus on local and regional areas of concern and should result in decisions based on what is
best for a specific location. With NEBA comes the recognition that, regardless of the response option chosen, some impact will
1
This guide is under the jurisdiction of ASTM Committee F20 on Hazardous Substances and Oil Spill Response and is the direct responsibility of Subcommittee F20.13
on Treatment.
Current edition approved April 1, 2006Dec. 1, 2013. Published April 2006January 2014. Originally approved in 2006. Last previous edition approved in 2006 as F2532–06.
DOI: 10.1520/F2532-06.10.1520/F2532-13.
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 ----------------------
F2532 − 13
occur. Tables 1 and 2Table 1 and Table 2 and Appendix X1 and Appendix X4 provide considerations for use in the NEBA process.
Appendix X2 and Appendix X3 present an ecological risk assessment method for determining the net environmental benefit of
dispersant use.
3
4.2 The NEBA process involves several tasks (1, 2).
4.2.1 Gather information on habitats and species of concern,
...

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1.3 This is a general guide only. It is assumed that conditions at the spill site have been assessed and that these conditions are suitable for the use of cleaning agents. It is assumed that permission has been obtained to use the chemical agents. Variations in the behavior of different types of oil are not dealt with in this guide and may change some of the parameters noted herein.  
1.4 This guide covers two different types of shoreline cleaners: those that disperse oil into the water and those that disperse little oil into the water under low energy levels. The selection criteria for these two types can differ widely. This guide does not cover dispersants.  
1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.  
1.6 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.7 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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ASTM
ASTM F1693-21(Guide)
Standard Guide for Consideration of Bioremediation as an Oil Spill Response Method on Land

SIGNIFICANCE AND USE
3.1 The purpose of this guide is to provide remediation managers and spill response teams with guidance on bioremediation.  
3.2 Bioremediation is one of many available tools and may not be applicable to all situations. This guide can be used in conjunction with other ASTM guides addressing oil spill response operations.
SCOPE
1.1 The goal of this guide is to provide recommendations for the use of biodegradation enhancing agents for remediating oil spills in terrestrial environments.  
1.2 This is a general guide only, assuming the bioremediation agent to be safe, effective, available, and applied in accordance with both manufacturers' recommendations and relevant environmental regulations. As referred to in this guide, oil includes crude and refined petroleum products.  
1.3 This guide addresses the application of bioremediation agents alone or in conjunction with other technologies, following spills on surface terrestrial environments.  
1.4 This guide does not consider the ecological effects of bioremediation agents.  
1.5 This guide applies to all terrestrial environments. Specifically, it addresses various technological applications used in these environments.  
1.6 In making bioremediation-use decisions, appropriate government authorities must be consulted as required by law.  
1.7 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. In addition, it is the responsibility of the user to ensure that such activity takes place under the control and direction of a qualified person with full knowledge of any potential or appropriate safety and health protocols.  
1.8 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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ASTM
ASTM F1778-97(2020)(Guide)
Standard Guide for Selection of Skimmers for Oil-Spill Response

SIGNIFICANCE AND USE
4.1 This guide is intended to facilitate the oil spill response equipment selection process for local, regional, and national spill response teams. It is not intended to define rigid sets of equipment standards.  
4.2 The effectiveness of the equipment chosen to combat an oil spill will depend on the oil type and environment(s) encountered, as well as other factors. This guide is intended to be used by persons generally familiar with the practical aspects of oil spill cleanup operations including on-scene response coordinators, planners, oil spill management teams, oil spill removal organizations, and plan evaluators.  
4.3 Eleven general types of skimming systems are described in this guide. Each description includes a summary of the operating principle and a list of selection considerations.  
4.4 Selection considerations are included to guide the user on the selection of a particular skimmer type or category. Users are cautioned that within each category there may be a wide variation in performance among various skimmers.  
4.5 When selecting a skimmer for use in extremely cold conditions, consideration should be given to the effect of ice forming on the skimmer, changes in buoyancy, possible restriction of inlets, and changes to hydraulic efficiency. Because there may be wide variations in skimmer performance at extreme temperatures, even within a given category, ambient temperature is not included as a selection consideration.
SCOPE
1.1 This guide covers considerations for selecting skimmer systems for the recovery of marine-oil spills. The purpose of this guide is to provide oil spill response planners, equipment manufacturers, users, and government agencies with a standard on the equipment selection process for the removal of oil from the marine environment.  
1.2 This guide does not address the compatibility of spill-control equipment with spill products. It is the user's responsibility to ensure that any equipment selected is compatible with anticipated products and conditions.  
1.3 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.  
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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