Significance and Use
Identification of the source of a spilled oil is established by comparison with known oils selected because of their possible relationship to the spill, that is, potential sources. Generally, the suspected source oils are from pipelines, tanks, etc., and therefore pose little problems in sampling compared to the spilled oil. This practice addresses the sampling of spilled oils in particular, but could be applied to appropriate source situations, for example, a ship's bilge.
1. Scope
1.1 These practices describe the procedures to be used in collecting samples of waterborne oils (see Practice D3415), oil found on adjoining shorelines, or oil-soaked debris, for comparison of oils by spectroscopic and chromatographic techniques, and for elemental analyses.
1.2 Two practices are described. Practice A involves “grab sampling” macro oil samples. Practice B can be used to sample most types of waterborne oils and is particularly applicable in sampling thin oil films or slicks. Practice selection will be dictated by the physical characteristics and the location of the spilled oil. These two practices are:
2. Referenced Documents (purchase separately)
The documents listed below are referenced within the subject standard but are not provided as part of the standard.
ASTM Standards
D1129 Terminology Relating to Water
D3415 Practice for Identification of Waterborne Oils
Keywords
oil identification; sampling; spilled oil; TFE-fluorocarbon polymer sampler; waterborne petroleum oils; Field testing--water; Petroleum oils; Sampling water analysis applications; Waterborne oils;
ICS Code
ICS Number Code 75.040 (Crude petroleum)
DOI: 10.1520/D4489-95R11
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Citing ASTM Standards
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