ASTM D5272-1992(1999) Standard Practice for Outdoor Exposure Testing of Photodegradable Plastics《可光降解塑料制品的室外曝光检验》.pdf
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1、Designation: D 5272 92 (Reapproved 1999)Standard Practice forOutdoor Exposure Testing of Photodegradable Plastics1This standard is issued under the fixed designation D 5272; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year
2、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 defines test conditions applicable whenPractices D 1435 and G 7 are employed for the outdoorexposure
3、 testing of photodegradable plastics.1.2 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 applica-bility of regulatory lim
4、itations prior to use.NOTE 1There is no ISO standard that is equivalent to this standard.2. Referenced Documents2.1 ASTM Standards:D 882 Test Methods for Tensile Properties of Thin PlasticSheeting2D 883 Terminology Relating to Plastics2D 1435 Practice for Outdoor Weathering of Plastics2D 1898 Practi
5、ce for Sampling of Plastics2D 3593 Test Method for Molecular Weight Averages andMolecular Weight Distribution of Certain Polymers byLiquid Size-Exclusion Chromatography (Gel PermeationChromatograph GPC) Using Universal Calibration3D 3826 Practice for Determining Degradation End Point inDegradable Po
6、lyolefins Using a Tensile Test3E 772 Terminology Relating to Solar Energy Conversion4G 7 Practice for Atmospheric Environmental ExposureTesting of Nonmetallic Materials53. Terminology3.1 The terminology given in Terminology E 772 and Ter-minology D 883 is applicable to this practice.4. Significance
7、and Use4.1 When discarded as litter, articles made using photode-gradable plastics are subject to attack by daylight (particularlysolar-ultraviolet radiation), oxygen, heat, and water. The 5exposure angle used in this practice represents typical condi-tions for degradation experienced by litter.4.2
8、This practice requires characterization of the duration ofexposure in terms of solar-ultraviolet radiation. Solar-ultraviolet radiation varies considerably as a function oflocation and time of year. This can cause dramatic differencesin the time required to produce a specified level of degradationin
9、 a polymer. Daro6has shown that when the same lot ofpolyethylene containing an iron-salt prodegradant is exposed atvarious times of the year in a single location, the time requiredto produce an average of two chain scissions per moleculevaried by over 130 %. Daro, and Zerlaut and Anderson7haveshown
10、that this variability can be significantly reduced whentotal solar or solar-ultraviolet radiation, or both, is used tocharacterize the exposure increments.4.3 In addition to variations in level of daylight and solar-ultraviolet radiation, there are significant differences in tem-perature, and moistu
11、re stresses between different locations, andbetween different years, or periods within a single year, at asingle location. Because of this variability, results from this testcannot be used to predict the absolute rate at which photode-gradable plastics degrade. Results from this test can be used toc
12、ompare relative rates of degradation for materials exposed atthe same time in the same location. Results from multipleexposures of a common lot of material (during differentseasons over several years) at different sites can be used tocompare the relative rates at which a particular photodegrad-able
13、plastic will degrade in each location.NOTE 2An inherent limitation in solar-radiation measurements is thatthey do not reflect the effects of variations in temperature and moistureexposure, which often can be as important as solar radiation. The samesolar-ultraviolet radiation increment will not nece
14、ssarily give the samechanges in properties of the test specimen in different exposure sites.Results from this practice must be regarded as giving only a generalindication of the degree of degradability and should always be consideredin terms of characteristics of the exposure site as well.4.4 Where
15、measurement of total solar-ultraviolet radiationis not possible, exposure duration can be determined by the1This practice is under the jurisdiction of ASTM Committee D-20 on Plasticsand is the direct responsibility of Subcommittee D20.96 on EnvironmentallyDegradable Plastics.Current edition approved
16、 July 15, 1992. Published September 1992.2Annual Book of ASTM Standards, Vol 08.01.3Annual Book of ASTM Standards, Vol 08.02.4Annual Book of ASTM Standards, Vol 12.02.5Annual Book of ASTM Standards, Vol 14.02.6Daro, A., et al, “Degradation of Polymer Blends IV, Natural Weathering of LowDensity and L
17、inear Low Density Polyethylene,” European Polymer Journal, Vol 26,No. 1, 1990, pp. 4752.7Zerlaut, G. L., and Anderson, T. A., “Ultraviolet Radiation as a TimingTechnique for Outdoor Weathering of Materials,” Society of Automotive Engineers,SAE Technical Paper Number 850348, 1985.1Copyright ASTM Inte
18、rnational, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.number of days, weeks, or months exposed. When this practiceis used, a reference material whose degradation properties havebeen well established must be exposed at the same time as theother materials being
19、 tested. The reference material used mustbe agreed upon by all interested parties. The time to produce aspecified level of degradation for each material in this simul-taneous exposure is then compared. It is also a good practice touse reference materials when exposure length is determined bytotal so
20、lar or solar UV radiant exposure.NOTE 3A reference material can be a single lot of material which hasshown consistent results after a number of exposures. It is not necessarythat the composition or properties of the reference material be character-ized and certified by a recognized standards agency
21、or group.5. Apparatus5.1 Use exposure racks constructed in accordance with therequirements of Practice G 7. Unless otherwise specified,position the exposure racks so that specimens face the equatorand so that the exposed surfaces are 5 from the horizontal. Ifother exposure rack orientations are used
22、, they must bereported.5.2 Use one of the following rack constructions for expos-ing photodegradable plastic specimens:5.2.1 Exposure Rack APositionable mounting bars usedfor attaching specimens shall be arrayed over a regular meshexpanded-metal (aluminum or stainless steel) sheet backing.Use 1618 g
23、age metal with approximately 0.5-in. openings. Itis recommended that the surface area of the expanded metal be60 to 70 % open. Use a noncorroding material for the mountingbars. 6061T6 aluminum or untreated wood are typical materi-als used for the mounting bars. Fig. 1 is a top view showingtypical ra
24、ck construction.5.2.2 Exposure Rack BUnpainted exterior-grade plywoodforms the rack surface to which specimens are directly at-tached. Replace the plywood when there is any evidence ofdelamination or fiber separation which could produce sharpedges and damage exposed specimens. Medium-density over-la
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