ASTM D5991-09
(Practice)Standard Practice for Separation and Identification of Poly(Vinyl Chloride) (PVC) Contamination in Poly(Ethylene Terephthalate) (PET) Flake
Standard Practice for Separation and Identification of Poly(Vinyl Chloride) (PVC) Contamination in Poly(Ethylene Terephthalate) (PET) Flake
SIGNIFICANCE AND USE
Presence of even low concentrations of PVC in recycled PET flakes may result in equipment corrosion problems during processing. The level of PVC contamination may also dictate the market for use of the recycled polymer in secondary products. Procedures presented in this practice are used to identify and, if desired, estimate the concentration of PVC contamination in recycled PET flakes.
SCOPE
1.1 This practice covers four procedures for separation and qualitative identification of poly(vinyl chloride) (PVC) contamination in poly(ethylene terephthalate) (PET) flakes.
Note 1—Although not presented as a quantitative method, procedures presented in this practice may be used to provide quantitative results at the discretion of the user. The user assumes the responsibility to verify the reproducibility of quantitative results. Data from an independent source suggest a PVC detection level of 200 ppm (w/w) based on an original sample weight of 454 g.
1.2 Procedure A is based on different fluorescence of PVC and PET when these polymers are exposed to ultraviolet (UV) light.
1.3 Procedure B is an oven test based upon the charring of PVC when it is heated in air at 235°C.
1.4 Procedures C and D are dye tests based on differential staining of PVC and PET.
Note 2—Other polymers (for example, PETG) also absorb the stain or brightener. Such interferences will result in false positive identification of PVC as the contaminant.
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 and health practices and determine the applicability of regulatory limitations prior to use. For specific hazards see Section 8.
Note 3—There is no known ISO equivalent to this practice.
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Designation:D5991 −09
StandardPractice for
Separation and Identification of Poly(Vinyl Chloride) (PVC)
1
Contamination in Poly(Ethylene Terephthalate) (PET) Flake
This standard is issued under the fixed designation D5991; 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 (´) indicates an editorial change since the last revision or reapproval.
1. Scope* D7209 Guide for Waste Reduction, Resource Recovery, and
Use of Recycled Polymeric Materials and Products
1.1 This practice covers four procedures for separation and
IEEE/ASTM SI-10 American National Standard for Use of
qualitative identification of poly(vinyl chloride) (PVC) con-
theInternationalSystemofUnits(SI):TheModernMetric
tamination in poly(ethylene terephthalate) (PET) flakes.
System
NOTE 1—Although not presented as a quantitative method, procedures
presentedinthispracticemaybeusedtoprovidequantitativeresultsatthe
3. Terminology
discretion of the user. The user assumes the responsibility to verify the
reproducibility of quantitative results. Data from an independent source
3.1 The terminology used in this practice is in accordance
suggest a PVC detection level of 200 ppm (w/w) based on an original
withTerminologyD1600andGuideD7209.Unitsandsymbols
sample weight of 454 g.
are in accordance with IEEE/ASTM SI-10.
1.2 Procedure A is based on different fluorescence of PVC
3.2 Definitions of Terms Specific to This Standard:
and PET when these polymers are exposed to ultraviolet (UV)
light. 3.2.1 light material, n—paper, polymers such as polyethyl-
ene and polypropylene, and other materials with densities less
1.3 Procedure B is an oven test based upon the charring of
3
than 1.00 g/cm .
PVC when it is heated in air at 235°C.
1.4 Procedures C and D are dye tests based on differential
4. Summary of Practice
staining of PVC and PET.
4.1 For the Beilstein Test, chlorine-containing materials
NOTE 2—Other polymers (for example, PETG) also absorb the stain or
heated in a flame in contact with a copper wire produce a
brightener. Such interferences will result in false positive identification of
characteristic green flame.
PVC as the contaminant.
1.5 This standard does not purport to address all of the
4.2 With Procedure A, a known amount of PET flakes is
safety concerns, if any, associated with its use. It is the
exposed to ultraviolet radiation. PET normally fluoresces with
responsibility of the user of this standard to establish appro-
a blue or violet color. Flakes fluorescing with different colors
priate safety and health practices and determine the applica-
are removed, weighed, and identified as PVC if they burn with
bilityofregulatorylimitationspriortouse.Forspecifichazards
a bright green flame when heated on a copper wire.
see Section 8.
4.3 With Procedure B, PET flakes are heated in an oven
NOTE 3—There is no known ISO equivalent to this practice.
maintained at 235 6 5°C.After 45 min, the flakes are visually
examined with removal and subsequent weighing of black,
2. Referenced Documents
charred pieces. Pieces are confirmed as PVC using the same
2
2.1 ASTM Standards:
flame test mentioned in 4.1.
D1600 TerminologyforAbbreviatedTermsRelatingtoPlas-
4.4 With Procedure C, PET flakes are soaked in a blue
tics
acetone 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 is
1
ThispracticeisunderthejurisdictionofASTMCommitteeD20onPlasticsand
is the direct responsibility of Subcommittee D20.95 on Recycled Plastics. confirmed with the flame test.
Current edition approved Feb. 1, 2009. Published February 2009. Originally
4.5 With Procedure D, PET flakes are heated with an
approved in 1996. Last previous edition approved in 2002 as D5991 - 96(2002).
DOI: 10.1520/D5991-09.
aqueous solution containing an optical brightener that also
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
preferentiallystainsthePVCflakes.Theflakesaresortedunder
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
UV light in a dark room with removal and subsequent
Standards volume information, refer to the standard’s Document Summary page on
the ASTM website. weighing of any blue fluorescing PVC flakes.
*A Summary of Changes section appears at the end of this standard
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1
---------------------- Page: 1 ----------------------
D5991−09
5. Significance and Use 8.2 Hot trays and flake samples should be handled with
thermally insulated gloves to avoid burns while placing trays
5.1 Presence of even low concentrations
...
This document is not anASTM standard and is intended only to provide the user of anASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation:D5991–96 (Reapproved 2002) Designation: D 5991 – 09
Standard Practice for
Separation and Identification of Poly(Vinyl Chloride) (PVC)
1
Contamination in Poly(Ethylene Terephthalate) (PET) Flake
This standard is issued under the fixed designation D 5991; 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 (´) indicates an editorial change since the last revision or reapproval.
1. Scope*
1.1 This practice covers four procedures for separation and qualitative identification of poly(vinyl chloride) (PVC)
contamination in poly(ethylene terephthalate) (PET) flakes.
NOTE 1—Although not presented as a quantitative method, procedures presented in this practice may be used to provide quantitative results at the
discretion of the user. The user assumes the responsibility to verify the reproducibility of quantitative results. Data from an independent source suggest
a PVC detection level of 200 ppm (w/w) based on an original sample weight of 454 g.
1.2 ProcedureA isbasedondifferentfluorescenceofPVCandPETwhenthesepolymersareexposedtoultraviolet(UV)light.
1.3 Procedure B is an oven test based upon the charring of PVC when it is heated in air at 235°C.
1.4 Procedures C and D are dye tests based on differential staining of PVC and PET.
NOTE 2—Other polymers (for example, PETG) also absorb the stain or brightener. Such interferences will result in false positive identification of PVC
as the contaminant.
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 and health practices and determine the applicability of regulatory
limitations prior to use. For specific hazards see Section 8.
NOTE3—There is no equivalent ISO standard. 3—There is no known ISO equivalent to this practice.
2. Referenced Documents
2
2.1 ASTM Standards:
D 1600 Terminology for Abbreviated Terms Relating to Plastics
2
D5033Guide for the Development of Standards Relating to the Proper Use of Recycled Plastics 7209 Guide for Waste
Reduction, Resource Recovery, and Use of Recycled Polymeric Materials and Products
E380Practice for Use of the International System of Units (SI) (the Modernized Metric System) IEEE/ASTM SI-10 American
National Standard for Use
of the International System
of Units (SI): The Modern
Metric System
3. Terminology
3.1 The terminology used in this practice is in accordance with Terminology D 1600 and Guide D5033D 7209. Units and
symbols are in accordance with Practice E380IEEE/ASTM SI-10.
3.2 Definitions of Terms Specific to This Standard:
3.2.1 light material, n—paper, polymers such as polyethylene and polypropylene, and other materials with densities less than
3
1.00 g/cm .
4. Summary of Practice
4.1 For the BeilsteinTest, chlorine-containing materials heated in a flame in contact with a copper wire produce a characteristic
green flame.
4.2 With ProcedureA, a known amount of PET flakes is exposed to ultraviolet radiation. PET normally fluoresces with a blue
1
This practice is under the jurisdiction of ASTM Committee D20 on Plastics and is the direct responsibility of Subcommittee D20.95 on Recycled Plastics .
Current edition approved July 10, 1996. Published September 1996.
Current edition approved Feb. 1, 2009. Published February 2009. Originally approved in 1996. Last previous edition approved in 2002 as D 5991 - 96(2002).
2
For referencedASTM standards, visit theASTM website, www.astm.org, or contactASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
, Vol 08.03.volume information, refer to the standard’s Document Summary page on the ASTM website.
*A Summary of Changes section appears at the end of this standard.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1
---------------------- Page: 1 ----------------------
D5991–09
or violet color. Flakes fluorescing with different colors are removed, weighed, and identified as PVC if they burn with a bright
green flame when heated on a copper wire.
4.3 WithProcedureB,PETflakesareheatedinanovenmaintainedat235 65°C.After45min,theflakesarevisuallyexamined
with removal and subsequent weighing of black, charred pieces. Pieces are confirmed as PVC using the same flame test mentioned
in 4.1.
4.4 With Procedure C, PET flakes are soaked in a blue acetone dye solution tha
...
This document is not anASTM standard and is intended only to provide the user of anASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation:D5991–96 (Reapproved 2002) Designation: D 5991 – 09
Standard Practice for
Separation and Identification of Poly(Vinyl Chloride) (PVC)
1
Contamination in Poly(Ethylene Terephthalate) (PET) Flake
This standard is issued under the fixed designation D 5991; 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 (´) indicates an editorial change since the last revision or reapproval.
1. Scope*
1.1 This practice covers four procedures for separation and qualitative identification of poly(vinyl chloride) (PVC)
contamination in poly(ethylene terephthalate) (PET) flakes.
NOTE 1—Although not presented as a quantitative method, procedures presented in this practice may be used to provide quantitative results at the
discretion of the user. The user assumes the responsibility to verify the reproducibility of quantitative results. Data from an independent source suggest
a PVC detection level of 200 ppm (w/w) based on an original sample weight of 454 g.
1.2 ProcedureA isbasedondifferentfluorescenceofPVCandPETwhenthesepolymersareexposedtoultraviolet(UV)light.
1.3 Procedure B is an oven test based upon the charring of PVC when it is heated in air at 235°C.
1.4 Procedures C and D are dye tests based on differential staining of PVC and PET.
NOTE 2—Other polymers (for example, PETG) also absorb the stain or brightener. Such interferences will result in false positive identification of PVC
as the contaminant.
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 and health practices and determine the applicability of regulatory
limitations prior to use. For specific hazards see Section 8.
NOTE3—There is no equivalent ISO standard. 3—There is no known ISO equivalent to this practice.
2. Referenced Documents
2
2.1 ASTM Standards:
D 1600 Terminology for Abbreviated Terms Relating to Plastics
2
D5033Guide for the Development of Standards Relating to the Proper Use of Recycled Plastics 7209 Guide for Waste
Reduction, Resource Recovery, and Use of Recycled Polymeric Materials and Products
E380Practice for Use of the International System of Units (SI) (the Modernized Metric System) IEEE/ASTM SI-10 American
National Standard for Use
of the International System
of Units (SI): The Modern
Metric System
3. Terminology
3.1 The terminology used in this practice is in accordance with Terminology D 1600 and Guide D5033D 7209. Units and
symbols are in accordance with Practice E380IEEE/ASTM SI-10.
3.2 Definitions of Terms Specific to This Standard:
3.2.1 light material, n—paper, polymers such as polyethylene and polypropylene, and other materials with densities less than
3
1.00 g/cm .
4. Summary of Practice
4.1 For the BeilsteinTest, chlorine-containing materials heated in a flame in contact with a copper wire produce a characteristic
green flame.
4.2 With ProcedureA, a known amount of PET flakes is exposed to ultraviolet radiation. PET normally fluoresces with a blue
1
This practice is under the jurisdiction of ASTM Committee D20 on Plastics and is the direct responsibility of Subcommittee D20.95 on Recycled Plastics.
Current edition approved July 10, 1996. Published September 1996.
Current edition approved Feb. 1, 2009. Published February 2009. Originally approved in 1996. Last previous edition approved in 2002 as D 5991 - 96(2002).
2
For referencedASTM standards, visit theASTM website, www.astm.org, or contactASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
, Vol 08.03.volume information, refer to the standard’s Document Summary page on the ASTM website.
*A Summary of Changes section appears at the end of this standard.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1
---------------------- Page: 1 ----------------------
D5991–09
or violet color. Flakes fluorescing with different colors are removed, weighed, and identified as PVC if they burn with a bright
green flame when heated on a copper wire.
4.3 WithProcedureB,PETflakesareheatedinanovenmaintainedat235 65°C.After45min,theflakesarevisuallyexamined
with removal and subsequent weighing of black, charred pieces. Pieces are confirmed as PVC using the same flame test mentioned
in 4.1.
4.4 With Procedure C, PET flakes are soaked in a blue acetone dye solution that
...












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