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STODDARD SOLVENT 67-8<br />

67.1 MAJOR USES AND COMPOSITION<br />

67.1.1 Major Uses<br />

Stoddard solvent is produced from a straight-run distillate of<br />

paraffinic or mixed base crude oil. It is used as a diluent in paints,<br />

coatings <strong>and</strong> waxes; as a dry cleaning agent: as a degreaser <strong>and</strong> cleaner<br />

<strong>and</strong> as a herbicide (2).<br />

67.1.2 Composition<br />

Stoddard solvent is a mixture of C, through C,, hydrocarbons,<br />

predominantly C, through C,,, with a boiling range between 16O'C to<br />

21O'C. Flashpoint dry-point test <strong>and</strong> odor data are used to classify<br />

Stoddard solvent into the following four types: regular Stoddard<br />

solvent, 140 flash solvent, odorless solvent, <strong>and</strong> low end point<br />

solvent. Chemically, Stoddsrd solvent is a mixture of 30-50% straight<br />

<strong>and</strong> branched alkanes, 30-40% cycloalkanes, <strong>and</strong> lo-20% aromatics.<br />

Benzene <strong>and</strong> olefins are present in trace quantities only (1967,2228).<br />

The 140 flash aliphatic solvent is composed of organic compounds with<br />

carbon chain lengths ranging from CS to C12. Its boiling range is<br />

185-207'C <strong>and</strong> it is composed of 60.8% paraffins, 24.5%<br />

monocycloparaffins, 11.2% dicycloparaffins, 3.03% alkyl benzenes, 0.3%<br />

indans <strong>and</strong> tetralins, <strong>and</strong> 0.07% benzenes (1967). Both types will be<br />

discussed in some sections of the chapter which follows.<br />

A characterization of the individual hydrocarbon components of<br />

Stoddard solvent was not available. Table 67-l presents the available<br />

characterization by chemical classes.<br />

67.2 ENVIRONMENTAL FATE AND EXPOSURE PATHWAYS<br />

A discussion of the environmental behavior of Stoddard solvent is<br />

limited by the lack of analytical data defining its specific<br />

components. Many of the hydrocarbons expected to be components of<br />

Stoddard solvent were addressed previously in the more extensive<br />

environmental fate section of ChapteE 64. The general discussions of<br />

aliphatfc <strong>and</strong> aromatic hydrocarbons <strong>and</strong> their behavior in<br />

soil/ground-water systems will not be repeated here: the reader is<br />

referred to the relevant sections of Chapter 64.<br />

67.2.1 Equilibrium Partitioning Model<br />

.In general, soil/ground-water transport pathways for low<br />

concentrations of pollutants in soil can be assessed by using an<br />

equilibrium partitioning model. For the purposes of assessing the<br />

,environmental transport of Stoddard solvent, a group of specific<br />

hydrocarbons within the c,-cl, range was selected from the dominant<br />

hydrocarbon classes, i.e., alkanes, cycloalkanes, <strong>and</strong> aromatics; there<br />

are no available data to confirm the presence of the selected<br />

6/87

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