ASTM D6288-1998(2003) Standard Practice for Separation and Washing of Recycled Plastics Prior to Testing《试验前回收塑料的清洗和分离的标准操作规程》.pdf
《ASTM D6288-1998(2003) Standard Practice for Separation and Washing of Recycled Plastics Prior to Testing《试验前回收塑料的清洗和分离的标准操作规程》.pdf》由会员分享,可在线阅读,更多相关《ASTM D6288-1998(2003) Standard Practice for Separation and Washing of Recycled Plastics Prior to Testing《试验前回收塑料的清洗和分离的标准操作规程》.pdf(3页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D 6288 98 (Reapproved 2003)Standard Practice forSeparation and Washing of Recycled Plastics Prior toTesting1This standard is issued under the fixed designation D 6288; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, th
2、e year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. Scope1.1 The practice describes a procedure for separating re-cycled plastics based on their color (for example, gre
3、en versuscolorless) and a procedure for washing dirty, ground plasticwhich results in separation of light materials (density 1.00g/cm3). This practice is not intended to represent genericwashing procedures used in the plastics recycling industry. Thedescribed procedures are solely for preparation of
4、 plasticsamples for use in other analytical tests. The procedureincludes a room temperature wash step to facilitate separationof paper (for example, labels) followed by washing at anelevated temperature.NOTE 1Although not presented as a quantitative method, the proce-dure presented in this practice
5、may be used to provide quantitative results.The user assumes the responsibility to verify the reproducibility ofquantitative results.1.2 The values stated in SI units are to be regarded as thestandard.1.3 This standard does not purport to address all of thesafety concerns, if any, associated with it
6、s use. It is theresponsibility of the user of this standard to establish appro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use.NOTE 2There is no equivalent ISO standard.2. Referenced Documents2.1 ASTM Standards:D 1600 Terminology for Abbrevi
7、ated Terms Relating toPlastics2D 5033 Guide for the Development of Standards Relating tothe Proper Use of Recycled Plastics3D 5814 Practice for Determination of Contamination inRecycled Poly(Ethylene Terephthalate) (PET) Flakes andChips Using a Plaque Test3E 5991 Practice for Separation and Identifi
8、cation of Poly-(Vinyl Chloride) (PVC) Contamination in Poly(EthyleneTerephthalate) (PET) Flake3IEEE/ASTM SI 10 Standard for Use of the InternationalSystem of Units (SI): The Modern Metric System43. Terminology3.1 The terminology used in this practice is in accordancewith Terminology D 1600 and Guide
9、 D 5033. Units andsymbols are in accordance with Standard IEEE/ASTM SI 10.3.2 Definitions of Terms Specific to This Standard:3.2.1 light materialpaper, polymers such as polyethyleneand polypropylene, and other materials with densities less than1.00 g/cm3.4. Summary4.1 Different colored (for example,
10、 green versus colorless)plastic materials are readily distinguished by visual inspectionof a sample.4.2 Labels, glue residues and other plastics may absorb thedyes used in some procedures for identifying contaminants orthese other contaminants may exhibit interfering fluorescence.Consequently, a sta
11、ndard procedure is provided for washingthe plastic prior to examination by these tests.4.3 This practice utilizes a room temperature wash step tofacilitate separation of paper (for example, labels) followed bywashing at an elevated temperature to permit separation ofplastics and other contaminants b
12、ased on densities. The roomtemperature wash step effectively removes labels withoutactivating some adhesives.NOTE 3The dye and fluorescence tests that may require plasticwashed by this procedure are specifically designed to detect poly(vinylchloride) (PVC) contamination.4.4 Washed recycled plastic m
13、aterials are then used for testssuch as those described in Practices D 5814 or D 5991.5. Significance and Use5.1 Dirt, paper and mixtures of polymeric materials com-plicate the interpretation of data from procedures used toidentify and, if desired, quantify the contaminants in recycledplastics.1This
14、 practice is under the jurisdiction of ASTM Committee D20 on Plastics andis the direct responsibility of Subcommittee D20.95 on Recycled Plastics.Current edition approved July 10, 2003. Published September 2003. Originallyapproved in 1998. Last previous edition approved in 1998 as D 6288 - 98.2Annua
15、l Book of ASTM Standards, Vol 08.01.3Annual Book of ASTM Standards, Vol 08.03.4Annual Book of ASTM Standards, Vol 14.02.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.6. Apparatus6.1 Bright Aluminum Tray, shallow depth (750 mm), wit
16、hminimum area of 774 cm2120 in.2.6.2 Balances, suitable for weighing 500 g of flake.6.3 Baffled Beaker, stainless steel, 15.2 cm 6 in. diameterwith four 1.9 cm 0.75 in. baffles providing a slurry height/diameter ratio of 0.9.6.4 Cover for Beaker (see 6.3) which can accommodate athermometer (or other
17、 temperature sensing device) and thestirring impeller rod.6.5 Overhead Stirrer, capable of 1000 r/min.6.6 Stirring Impeller, pitched three blade, 7.62 cm 3 in.diameter.6.7 Plastic Pails, 19 L 5 gal.6.8 Strainer, non-aluminum to fit the pails described in 6.7.6.9 Hot Plate.6.10 Thermometer.6.11 Manua
18、l Stirring Rod.6.12 Oven, capable of drying plastic flakes at 60 6 2C.7. Materials7.1 Water, distilled or deionized.7.2 Sodium Hydroxide, granular.7.3 Detergent, nonionic surfactant.NOTE 4Nonylphenol or octylphenol derivatives are effective deter-gents for this procedure. Users of this procedure sho
19、uld be aware thatthese materials have been linked to endocrine/estrogen activity and falsepositive interferences with breast cancer research. Anionic detergents mayalso be effective.7.4 Wash solution, consisting of 2 L of water, 0.3 % (6 g)nonionic surfactant (see 7.3), and 1 % (20 g) sodium hydroxi
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