ASTM D6288-2009 6250 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实施规程》.pdf
《ASTM D6288-2009 6250 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实施规程》.pdf》由会员分享,可在线阅读,更多相关《ASTM D6288-2009 6250 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实施规程》.pdf(3页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D 6288 09Standard 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, the year of last rev
2、ision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon () indicates an editorial change since the last revision or reapproval.1. Scope*1.1 The practice describes a procedure for separating re-cycled plastics based on their color (for example, green versuscolorless
3、) 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 plasticsamples fo
4、r 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 may be used to pro
5、vide 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 its use. It is there
6、sponsibility 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 known ISO equivalent to this practice.2. Referenced Documents2.1 ASTM Standards:2D 1600 Terminology for Abbreviate
7、d Terms Relating toPlasticsD 5814 Practice for Determination of Contamination inRecycled Poly(Ethylene Terephthalate) (PET) Flakes andChips Using a Plaque TestD 5991 Practice for Separation and Identification of Poly-(Vinyl Chloride) (PVC) Contamination in Poly(EthyleneTerephthalate) (PET) FlakeD 72
8、09 Guide for Waste Reduction, Resource Recovery,and Use of Recycled Polymeric Materials and ProductsIEEE/ASTM SI 10 Standard for Use of the InternationalSystem of Units (SI): The Modern Metric System3. Terminology3.1 The terminology used in this practice is in accordancewith Terminology D 1600 and G
9、uide D 7209. 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 exam
10、ple, 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
11、 standard 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 contaminan
12、ts based 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.1This practice is under t
13、he jurisdiction ofASTM Committee D20 on Plastics andis the direct responsibility of Subcommittee D20.95 on Recycled Plastics.Current edition approved Sept. 1, 2009. Published September 2009. Originallyapproved in 1998. Last previous edition approved in 2003 as D 6288 - 98(2003).2For referenced ASTM
14、standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.1*A Summary of Changes section appears at the end of this standard.Copyright ASTM
15、International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.4.4 Washed recycled plastic materials 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
16、 the interpretation of data from procedures used toidentify and, if desired, quantify the contaminants in recycledplastics.6. Apparatus6.1 Bright Aluminum Tray, shallow depth (750 mm), withminimum area of 774 cm2(120 in.2).6.2 Balances, suitable for weighing 500 g of flake.6.3 Baffled Beaker, stainl
17、ess 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 temperature sensing device) and thestirring impeller rod.6.5 Overhead Stirrer, capable of 1000 r/min.6.6
18、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 Manual Stirring Rod.6.12 Oven, capable of drying plastic flakes at 60 6 2C.7. Materials7.1 Water, distilled
19、 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 should be aware thatthese materials have been linked to endocrine/estrogen activity and falsepositive int
20、erferences 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 hydroxide(see 7.2). Dissolve the surfactant in cold water prior to additionof the sodium hydroxide.8. Procedu
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