ASTM D5991-1996(2002) Standard Practice for Separation and Identification of Poly(Vinyl Chloride) (PVC) Contamination in Poly(Ethylene Terephthalate) (PET) Flake《聚乙烯对酞酰小片中聚氯乙烯污染的分离.pdf
《ASTM D5991-1996(2002) Standard Practice for Separation and Identification of Poly(Vinyl Chloride) (PVC) Contamination in Poly(Ethylene Terephthalate) (PET) Flake《聚乙烯对酞酰小片中聚氯乙烯污染的分离.pdf》由会员分享,可在线阅读,更多相关《ASTM D5991-1996(2002) Standard Practice for Separation and Identification of Poly(Vinyl Chloride) (PVC) Contamination in Poly(Ethylene Terephthalate) (PET) Flake《聚乙烯对酞酰小片中聚氯乙烯污染的分离.pdf(3页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D 5991 96 (Reapproved 2002)Standard Practice forSeparation and Identification of Poly(Vinyl Chloride) (PVC)Contamination in Poly(Ethylene Terephthalate) (PET) Flake1This standard is issued under the fixed designation D 5991; the number immediately following the designation indicates the
2、 year oforiginal adoption or, in the case of revision, the 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 This practice covers four procedures for separatio
3、n andqualitative identification of poly(vinyl chloride) (PVC) con-tamination in poly(ethylene terephthalate) (PET) flakes.NOTE 1Although not presented as a quantitative method, procedurespresented in this practice may be used to provide quantitative results at thediscretion of the user. The user ass
4、umes the responsibility to verify thereproducibility of quantitative results. Data from an independent sourcesuggest a PVC detection level of 200 ppm (w/w) based on an originalsample weight of 454 g.1.2 Procedure A is based on different fluorescence of PVCand PET when these polymers are exposed to u
5、ltraviolet (UV)light.1.3 Procedure B is an oven test based upon the charring ofPVC when it is heated in air at 235C.1.4 Procedures C and D are dye tests based on differentialstaining of PVC and PET.NOTE 2Other polymers (for example, PETG) also absorb the stain orbrightener. Such interferences will r
6、esult in false positive identification ofPVC as the contaminant.1.5 This standard does not purport to address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard to establish appro-priate safety and health practices and determine the appli
7、ca-bility of regulatory limitations prior to use. For specific hazardssee Section 8.NOTE 3There is no equivalent ISO standard.2. Referenced Documents2.1 ASTM Standards:D 1600 Terminology for Abbreviated Terms Relating toPlastics2D 5033 Guide for the Development of Standards Relating tothe Proper Use
8、 of Recycled Plastics2E 380 Practice for Use of the International System of Units(SI) (the Modernized Metric System)33. Terminology3.1 The terminology used in this practice is in accordancewith Terminology D 1600 and Guide D 5033. Units andsymbols are in accordance with Practice E 380.3.2 Definition
9、s of Terms Specific to This Standard:3.2.1 light material, npaper, polymers such as polyethyl-ene and polypropylene, and other materials with densities lessthan 1.00 g/cm3.4. Summary of Practice4.1 For the Beilstein Test, chlorine-containing materialsheated in a flame in contact with a copper wire p
10、roduce acharacteristic green flame.4.2 With Procedure A, a known amount of PET flakes isexposed to ultraviolet radiation. PET normally fluoresces witha blue or violet color. Flakes fluorescing with different colorsare removed, weighed, and identified as PVC if they burn witha bright green flame when
11、 heated on a copper wire.4.3 With Procedure B, PET flakes are heated in an ovenmaintained at 235 6 5C. After 45 min, the flakes are visuallyexamined with removal and subsequent weighing of black,charred pieces. Pieces are confirmed as PVC using the sameflame test mentioned in 4.1.4.4 With Procedure
12、C, PET flakes are soaked in a blueacetone dye solution that preferentially stains any PVC flakes.These flakes are visually identified and subsequently removed,and weighed. If desired, the identification of PVC flakes isconfirmed with the flame test.4.5 With Procedure D, PET flakes are heated with an
13、aqueous solution containing an optical brightener that alsopreferentially stains the PVC flakes. The flakes are sorted underUV light in a dark room with removal and subsequentweighing of any blue fluorescing PVC flakes.5. Significance and Use5.1 Presence of even low concentrations of PVC in recycled
14、PET flakes may result in equipment corrosion problems duringprocessing. The level of PVC contamination may also dictate1This 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
15、10, 1996. Published September 1996.2Annual Book of ASTM Standards, Vol 08.03.3Annual Book of ASTM Standards, Vol 14.02.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.the market for use of the recycled polymer in secondaryproducts. P
16、rocedures presented in this practice are used toidentify and, if desired, estimate the concentration of PVCcontamination in recycled PET flakes.6. Apparatus6.1 Procedure A:6.1.1 Bright Aluminum Tray, shallow depth (0.75 cm).6.1.2 Light Fixture, equipped with GE F40/BLB, or equiva-lent, black light b
17、ulbs.6.1.3 Ultraviolet Shield Glasses.6.1.4 Tweezers.6.2 Procedure B:6.2.1 Circulating or Forced-Air Oven, equipped with atemperature readout device for the range of 230 to 240C.6.2.2 Baking Trays,14by20by3cm.6.2.3 Tweezers.6.2.4 Thermally Insulated Gloves, or equivalent.6.3 Procedure C:6.3.1 Measur
18、ing Cup, 1.5 L.6.3.2 Plastic Stretch or Cling Wrap.6.3.3 Paper Towels, newspaper, or equivalent.6.3.4 Tweezers.6.4 Procedure D:6.4.1 Measuring Cup, 1.5 L.6.4.2 Tweezers.6.4.3 Hot Plate, or equivalent heating device.6.4.4 Light Fixture, equipped with GE F40/BLB, or equiva-lent, black light bulbs.6.4.
19、5 Ultraviolet Shield Glasses.7. Materials7.1 Detergent.7.2 Rity Tint and Dye (Navy Blue #30),4or equivalent,required for Procedure C.7.3 Rity Brightener and Whitener,4or equivalent, requiredfor Procedure D.8. Hazards8.1 The ultraviolet light used in Procedures A and D may beharmful to exposed skin a
20、nd unprotected eyes, so a UV filteringface shield or UV absorbing glasses should be worn whenperforming this test. Exposed hands and arms should becovered with gloves and long sleeves.8.2 Hot trays and flake samples should be handled withthermally insulated gloves to avoid burns while placing traysc
21、ontaining samples into or removing them from the oven(Procedure B).8.3 Acetone used to prepare the dye solution for ProcedureC is flammable. Use this reagent only in a well ventilated areafree of open flames or spark sources.9. Procedure9.1 Flame Test to Verify PVC Identification (Beilstein Test):9.
22、1.1 Heat a copper wire in a propane torch flame until it isvery hot.9.1.2 Touch the hot wire to a suspected PVC flake to melt asmall amount of the flake on to the wire.9.1.3 Reheat the wire tip in the flame. If the tested flake isPVC, a bright green flame will be visible as the wire heats andthe pla
23、stic burns. Absence of a green flame indicates that thetest flake is not PVC.9.2 Procedure A:9.2.1 Weigh 454 6 10 g of clean, dry PET flake sample andtransfer the sample into a shallow aluminum tray.9.2.2 Place the tray under the UV light in a dark environ-ment.9.2.3 Using tweezers, sort through the
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