• There are no items in your cart

PD CEN/TR 15522-2:2012

Superseded
Superseded

A superseded Standard is one, which is fully replaced by another Standard, which is a new edition of the same Standard.

View Superseded by
superseded

A superseded Standard is one, which is fully replaced by another Standard, which is a new edition of the same Standard.

Oil spill identification. Waterborne petroleum and petroleum products Analytical methodology and interpretation of results based on GC-FID and GC-MS low resolution analyses
Available format(s)

Hardcopy , PDF

Superseded date

04-13-2023

Language(s)

English

Published date

10-31-2012

Foreword
Introduction
1 Scope
2 Normative references
3 Terms, definitions and abbreviated terms
4 Strategy for the identification of oil spills
  sources
5 Sample preparation
6 Characterisation and evaluation of analytical data
Annex A (normative) - GC-FID analysis
Annex B (normative) - GC-MS analysis
Annex C (informative) - List of PAHs and biomarkers
        analysed by GC-MS-SIM
Annex D (informative) - Alkyl homologue patterns of
        PAHs
Annex E (informative) - Diagnostic ratios
Annex F (informative) - General composition of
        oils - chemical groups
Annex G (informative) - Weathering of oils spilled on
        water
Annex H (informative) - Characteristic Features of
        Different Oil Types in Oil Spill
        Identification
Annex I (informative) - Example of internal
        documentation - technical report
        of an oil spill case
Annex J (informative) - Example of external
        documentation - identification report
        of an oil spill identification case
Bibliography

Provides a methodology to firstly identify the specific nature of oils spilled in marine, estuarine and aquatic environments and secondly compare the chemical composition of spilled oil or oily samples with that of suspected sources.

This Technical Report (TR) describes a methodology to firstly identify the specific nature of oils spilled in marine, estuarine and aquatic environments and secondly compare the chemical composition of spilled oil or oily samples with that of suspected sources. Specifically, the TR describes the detailed analytical methods and data processing specifications for identifying the specific nature of waterborne oil spills and establishing their correlation to suspected sources. Even when samples or data from suspected sources are not available for comparison, establishing the specific nature (e.g., refined petroleum, crude oil, waste oil, etc.) of the spilled oil may still help constrain the possible source(s) of the spilled oil.

This methodology is restricted to petroleum and petroleum products containing a significant proportion of hydrocarbon-components with a boiling point above 200°C. Examples are: crude oils, higher boiling condensates, diesel oils, residual bunker or heavy fuel oils, lubricants, and mixtures of bilge and sludge samples. While the specific analytical methods may not be appropriate for lower boiling oils (e.g. kerosenes, jet fuels, or gasoline), the general concepts described in this methodology, i.e., statistical comparison of weathering-resistant diagnostic ratios, may have applicability in spills involving lower boiling oils.

This method is not directly intended for oil spills impacting groundwater, vegetation, wildlife/tissues, soils, or sediments, and although its application in these matrices is not precluded, it requires caution. The reason for caution is that the extractable compounds in these matrices may alter and/or contribute additional compounds compared to the source sample, which if left unrecognised, can lead to “false non-matches”. Including these “non-oil” matrices in this oil spill identification method may require additional sample preparation (e.g. clean-up) in the laboratory prior to analysis and consideration of the extent to which the matrix may affect the correlation achieved. Evaluating the possible effects in these matrices is beyond the scope of this guideline. Whether the method can be used for this kind of “non-oil” matrices may depend on the oil concentration compared to the “matrix concentration” of the samples. In “non-oil” matrices containing a relative high concentration of oil, a positive match can still be concluded. In “non-oil” matrices containing a relative low concentration of spilled oil, a non-match or an inconclusive match could be achieved due to matrix effects.

Committee
PTI/12
DocumentType
Standard
Pages
142
PublisherName
British Standards Institution
Status
Superseded
SupersededBy
Supersedes

Standards Relationship
CEN/TR 15522-2:2012 Identical

ISO/IEC 17025:2005 General requirements for the competence of testing and calibration laboratories
ISO 5725-1:1994 Accuracy (trueness and precision) of measurement methods and results — Part 1: General principles and definitions
ISO 5725-6:1994 Accuracy (trueness and precision) of measurement methods and results — Part 6: Use in practice of accuracy values
ISO 5725-2:1994 Accuracy (trueness and precision) of measurement methods and results Part 2: Basic method for the determination of repeatability and reproducibility of a standard measurement method
CEN/TR 15522-1:2006 Oil spill identification - Waterborne petroleum and petroleum products - Part 1: Sampling

View more information
US$426.44
Excluding Tax where applicable

Access your standards online with a subscription

Features

  • Simple online access to standards, technical information and regulations.

  • Critical updates of standards and customisable alerts and notifications.

  • Multi-user online standards collection: secure, flexible and cost effective.