ASTM D2604-86(2000)
(Specification)Standard Specification for High-Boiling Hydrocarbon Solvent for Preparing Oil-Borne Preservative Solutions (Withdrawn 2006)
Standard Specification for High-Boiling Hydrocarbon Solvent for Preparing Oil-Borne Preservative Solutions (Withdrawn 2006)
SCOPE
1.1 This specification covers high-boiling hydrocarbon solvent for preparing solutions of oil-borne preservatives such as pentachlorophenol and copper naphthenate, and which shall be composed of petroleum distillates and cosolvents, provided that the blended solvent meets the requirements of Section 3.
WITHDRAWN RATIONALE
This specification covers high-boiling hydrocarbon solvent for preparing solutions of oil-borne preservatives such as pentachlorophenol and copper naphthenate, and which shall be composed of petroleum distillates and cosolvents.
Formerly under the jurisdiction of Committee D07 on Wood, this specification was withdrawn without replacement in July 2006.
General Information
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NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.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: D 2604 – 86 (Reapproved 2000)
Standard Specification for
High-Boiling Hydrocarbon Solvent for Preparing Oil-Borne
Preservative Solutions
This standard is issued under the fixed designation D 2604; 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 3. Properties
1.1 This specification covers high-boiling hydrocarbon sol- 3.1 High-boiling hydrocarbon solvent for preparing oil-
vent for preparing solutions of oil-borne preservatives such as borne preservative solutions shall conform to the following
pentachlorophenol and copper naphthenate, and which shall be requirements:
composed of petroleum distillates and cosolvents, provided
Distillation:
50 % volume distilling point, min° F 490
that the blended solvent meets the requirements of Section 3.
90 % volume distilling point, min° F 585
Viscosity of oil fraction undistilled above 500°F from 100-mL Method
2. Referenced Documents
D 86 distillation:
Kinematic, min, cSt at 100°F 3.46
2.1 ASTM Standards:
Saybolt, min, SUS at 100°F 37.5
D 86 Test Method for Distillation of Petroleum Products
Flash point, Pensky-Martens closed tester, min, °F 150
D 93 Test Methods for Flash-Point by Pensky-Martens
Solubility, pentachlorophenol at 75°F:
Minimum 90 g whole oil, g 10
Closed Cup Tester
Minimum in oil fraction undistilled above 500°F from a 100-mL 6
D 96 Test Methods for Water and Sediment in Crude Oil by
Method D 86 distillation
Centrifuge Method (Field Procedure) Water, max % 0.5
D 270 Method of Sampling Petroleum and Petroleum Prod-
4. Test Methods
ucts
4.1 The material shall be sampled and the properties enu-
D 287 TestMethodforAPIGravityofCrudePetroleumand
merated in this specification shall be determined in accordance
Petroleum Products (Hydrometer Method)
with the following ASTM methods:
D 445 Test Method for Kinematic Viscosity of Transparent
4.1.1 Sampling—Method D 270.
and Opaque Liquids (and the Calculation of Dynamic
4.1.2 Distillation—Test Method D 86.
Viscosity)
4.1.3 Viscosity—Test Method D 445.
D 2606 Test Method for Solubility of Pentachlorophenol in
4.1.4 Flash
...
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SIGNIFICANCE AND USE
3.1 Limitations have been established on formaldehyde emission levels for wood panel building products made with urea-formaldehyde adhesives and permanently installed in homes or used as components in kitchen cabinets and for similar industrial products. This test method is used in conjunction with the test method referenced by HUD Rules and Regulations 24 CFR 3280 for manufactured housing, California Air Resources Board (CARB) regulation 93120, EPA TSCA Title VI 40 CFR Section 770, and by Minnesota Statutes Section 144.495 for housing units and building materials. This test method provides a means of testing small-size samples to determine formaldehyde emission potential.
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3.2.1 Conditioning of panel products prior to testing,
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3.2.3 Test desiccator temperature, and
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SCOPE
1.1 This test method covers the laboratory evaluation of treated or untreated wood for its resistance to subterranean termites. This test is considered as a screening test for treated material and further evaluation by field methods is required.
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SIGNIFICANCE AND USE
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SIGNIFICANCE AND USE
4.1 This practice describes different methods of exposing fire-retardant-treated wood products or assemblies to controlled accelerated weathering or conditioning.
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SCOPE
1.1 This practice addresses the durability of a fire-retardant treatment of wood products by exposure to accelerated cycles of wetting, drying, or ultraviolet (UV) exposure, or combination thereof, prior to evaluation by a fire response test. Four conditioning methods are described.
1.2 This practice is applicable to wood products that have been treated with fire-retardant chemicals by pressure impregnation.
1.3 The test specimens are to be in the form of, or suitable for fabrication into, test specimens, such as those described in Test Methods E84, E108, and E1354 and other standard test methods for evaluating the fire performance of fire-retardant-treated wood products.
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5.1 Water is known to penetrate wood substrates, causing dimensional instability and eventual deterioration. Clear water repellent coatings are designed to protect wood from damaging effects of water. This test method is used to evaluate the effectiveness of water repellent coatings on wood soon after application or after long-term exterior exposure.
SCOPE
1.1 This test method evaluates the effectiveness of clear water repellent coatings on wood before or after exterior exposure.
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SCOPE
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SIGNIFICANCE AND USE
4.1 In past research experiments, some surface applied fire retardant chemicals improved the fire performance characteristics of natural Christmas trees, whereas other retardants were not effective, or adversely affected tree quality or burning characteristics. These methods are intended to provide a two-step process to determine the effectiveness of surface applied treatments to natural Christmas trees.
4.2 The fire performance of natural trees is highly variable and varies from species to species. Test results from these methods do not intend to provide data for judgment on the absolute fire performance of any natural or treated natural tree, but rather provide a means for comparing the fire performance of treated versus untreated trees.
4.3 These test methods do not take into account the influence of decorations that are added to the tree.
4.4 For Test Method 1, only Fraser fir [Abies fraseri (Pursh) Poi.] trees are tested. Although this is one of the most commonly used Christmas trees in the United States, it is possible that results for other tree species will differ from the results for this species.
4.5 For Test Method 2, Large Scale Fire Test, it is important that the treated and untreated tree specimens be evaluated consistently and as simultaneously as possible for adequate comparative results.
4.6 The performance of the treatment will vary depending on the uniformity of the application of the treatment. This quality of application is not determined by these test methods.
SCOPE
1.1 This fire-test-response standard provides a two-step testing process for determining the effectiveness of surface applied treatments for natural Christmas trees to improve fire test response. In order for a treatment to be considered compliant with this standard, the Conditions of Acceptance of both Methods 1 and 2 are to be met.
1.2 The purpose of these test methods is to:
1.2.1 Utilize a detached branch test (Method 1) to screen potential surface-applied fire retardant products and to determine their effectiveness in limiting the spread of flame and the continuation of flaming by comparing the burning characteristics of treated and untreated small Christmas tree branches subjected to a small open Bunsen-burner type flame ignition source, and
1.2.2 Use whole natural Christmas trees (Method 2) to determine the effectiveness of surface applied fire retardants found to be effective in the detached branch test (Method 1) through comparison of heat release rate contribution of treated trees as compared to untreated trees when subjected to an open flame ignition source.
1.3 The values stated in inch-pound units are to be regarded as standard. The values given in parentheses are mathematical conversions to SI units that are provided for information only and are not considered 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 Fire testing is inherently hazardous. Adequate safeguards for personnel and property shall be employed in conducting these tests.
1.6 The text of this standard references notes and footnotes which provide explanatory material. These notes and footnotes (excluding those in tables and figures) shall not be considered as requirements of the standard.
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SIGNIFICANCE AND USE
4.1 The effects of VOC sources on the indoor air quality in buildings have not been well established. One basic requirement that has emerged from indoor air quality studies is the need for well-characterized test data on the emission factors of VOCs from building materials. Standard test method and procedure are a requirement for the comparison of emission factor data from different products.
4.2 This practice describes a procedure for using a small environmental test chamber to determine the emission factors of VOCs from wood-based panels over a specified period of time. A pre-screening analysis procedure is also provided to identify the VOCs emitted from the products, to determine the appropriate GC-MS or GC-FID analytical procedure, and to estimate required sampling volume for the subsequent environmental chamber testing.
4.3 Test results obtained using this practice provide a basis for comparing the VOC emission characteristics of different wood-based panel products. The emission data can be used to inform manufacturers of the VOC emissions from their products. The data can also be used to identify building materials with reduced VOC emissions over the time interval of the test.
4.4 While emission factors determined by using this practice can be used to compare different products, the concentrations measured in the chamber shall not be considered as the resultant concentrations in an actual indoor environment.
SCOPE
1.1 The practice measures the volatile organic compounds (VOC), excluding formaldehyde, emitted from manufactured wood-based panels. A pre-screening analysis is used to identify the VOCs emitted from the panel. Emission factors (that is, emission rates per unit surface area) for the VOCs of interest are then determined by measuring the concentrations in a small environmental test chamber containing a specimen. The test chamber is ventilated at a constant air change rate under the standard environmental conditions. For formaldehyde determination, see Test Method D6007.
1.2 This practice describes a test method that is specific to the measurement of VOC emissions from newly manufactured individual wood-based panels, such as particleboard, plywood, and oriented strand board (OSB), for the purpose of comparing the emission characteristics of different products under the standard test condition. For general guidance on conducting small environmental chamber tests, see Guide D5116.
1.3 VOC concentrations in the environmental test chamber are determined by adsorption on an appropriate single adsorbent tube or multi-adsorbent tube, followed by thermal desorption and combined gas chromatograph/mass spectrometry (GC-MS) or gas chromatograph/flame ionization detection (GC-FID). The air sampling procedure and the analytical method recommended in this practice are generally valid for the identification and quantification of VOCs with saturation vapor pressure between 500 and 0.01 kPa at 25°C, depending on the selection of adsorbent(s).
Note 1: VOCs being captured by an adsorbent tube depend on the adsorbent(s) and sampling procedure selected (see Practice D6196). The user should have a thorough understanding of the limitations of each adsorbent used. Although canisters can be used to sample VOCs, this standard is limited to sampling VOCs from the chamber air using adsorbent tubes.
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SIGNIFICANCE AND USE
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SCOPE
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1.5 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.
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