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GB/T 43282.1-2023   Plastics—Determination of the aerobic biodegradation of plastic materials exposed to seawater—Part 1: Method by analysis of evolved carbon dioxide (English Version)
Standard No.: GB/T 43282.1-2023 Status:valid remind me the status change

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Standard No.: GB/T 43282.1-2023
English Name: Plastics—Determination of the aerobic biodegradation of plastic materials exposed to seawater—Part 1: Method by analysis of evolved carbon dioxide
Chinese Name: 塑料 暴露于海水中塑料材料需氧生物分解的测定 第1部分:采用分析释放二氧化碳的方法
Chinese Classification: G31    Basic standards and general methods for synthetic resin and plastic
Professional Classification: GB    National Standard
ICS Classification: 83.080.01 83.080.01    Plastics in general 83.080.01
Source Content Issued by: SAMR; SAC
Issued on: 2023-11-27
Implemented on: 2024-6-1
Status: valid
Target Language: English
File Format: PDF
Word Count: 10500 words
Translation Price(USD): 315.0
Delivery: via email in 1~3 business day
GB/T 43282.1-2023 Plastics - Determination of the aerobic biodegradation of plastic materials exposed to seawater - Part 1: Method by analysis of evolved carbon dioxide 1 Scope This document specifies a laboratory test method for determining the degree and rate of the aerobic biodegradation level of plastic materials. Biodegradation is determined by measuring the CO2 evolved from plastic materials when exposed to seawater sampled from coastal areas under laboratory conditions. The conditions described in this document might not always correspond to the optimum conditions for the maximum degree of biodegradation, however this test method is designed to give an indication of the potential biodegradability of plastic materials. Note: This document addresses plastic materials but can also be used for other materials. 2 Normative references The following documents are referred to in the text in such a way that some or all of their content constitutes requirements of this document. For dated references, only the edition cited applies. For undated references, the latest edition of the referenced document (including any amendments) applies. ISO 5667-3 Water quality - Sampling - Part 3: Preservation and handling of water samples ISO 8245 Water quality - Guidelines for the determination of total organic carbon (TOC) and dissolved organic carbon (DOC) ISO 10210 Plastics - Methods for the preparation of samples for biodegradation testing of plastic materials ISO 10523 Water quality - Determination of pH ISO 11261 Soil quality - Determination of total nitrogen - Modified Kjeldahl method 3 Terms and definitions For the purposes of this document, the following terms and definitions apply. 3.1 pelagic zone water body above the seafloor Note 1: It is also referred to as the open water or the water column. Note 2: The surface of the pelagic zone is moved by wind-driven waves, is in contact with the atmosphere and exposed to sunlight. With increasing depth pressure increases, temperature decreases, and light and surface wave energy are attenuated. [SOURCE: ISO 22766:2020, 3.4] 3.2 dissolved inorganic carbon; DIC part of the inorganic carbon in water which cannot be removed by specified phase separation Note: Phase separation can be achieved for example by centrifugation at 40000 m/s−2 for 15 min or by membrane filtration using membranes with pores of 0.2 μm to 0.45 μm diameter. [SOURCE: ISO 14852:2021, 3.4] 3.3 theoretical amount of evolved carbon dioxide; ThCO2 maximum theoretical amount of carbon dioxide evolved after completely oxidizing a chemical compound, calculated from the molecular formula Note: It is expressed as milligrams of carbon dioxide evolved per milligram or gram of test compound. [SOURCE: ISO 14852:2021, 3.5] 3.4 total organic carbon; TOC amount of carbon bound in an organic compound Notey: It is expressed as milligrams of carbon per 100 mg of the compound. [SOURCE: GB/T 40611-2021, 3.14] 3.5 dissolved organic carbon; DOC part of the organic carbon in water which cannot be removed by specified phase separation Note: Phase separation can be achieved for example by centrifugation at 40000 m/s−2 for 15 min or by membrane filtration using membranes with pores of 0.2 μm to 0.45 μm diameter. [SOURCE: ISO 14852:2021, 3.7] 3.6 lag phase time from the start of a test until adaptation and/or selection of the degrading microorganisms is achieved and the degree of biodegradation of a chemical compound or organic matter has increased to about 10 % of the maximum level of biodegradation (3.8) Note: It is measured in days. [SOURCE: ISO 14852:2021, 3.8] 3.7 biodegradation phase time from the end of the lag phase (3.6) of a test until the plateau phase has been reached Note: It is measured in days. [SOURCE: ISO 14852:2021, 3.10] 3.8 maximum level of biodegradation degree of biodegradation of a chemical compound or organic matter in a test, above which no further biodegradation takes place during the test Note: It is measured in per cent. [SOURCE: ISO 14852:2021, 3.9] 3.9 plateau phase time from the end of the biodegradation phase (3.7) until the end of a test Note: It is measured in days. [SOURCE: ISO 14852:2021, 3.11] 3.10 pre-conditioning pre-incubation of an inoculum under the conditions of the subsequent test in the absence of the chemical compound or organic matter under test, with the aim of improving the test by acclimatization of the microorganisms to the test conditions [SOURCE: ISO 14852:2021, 3.13] 4 Principle This document describes two variations of a test method for determining the biodegradability of plastic materials by the indigenous population of microorganisms in natural seawater using a static aqueous test system. The test is performed under mesophilic test conditions for up to two years by incubating plastic materials with either seawater only (“pelagic seawater test”) or with seawater to which low amount of sediment has been added (“suspended sediment seawater test”), coming from the same site as that from which the seawater was taken. Biodegradation is followed by measuring the evolution of carbon dioxide using a suitable, analytical method. The level of biodegradation is determined by comparing the amount of carbon dioxide evolved with the theoretical amount [theoretical amount of evolved carbon dioxide (ThCO2)] and expressed in percentage. The test result is the maximum level of biodegradation, determined from the plateau phase of the biodegradation curve. The principle of a system for measuring evolved carbon dioxide is given in ISO 14852:2021, Annex A.
Code of China
Standard
GB/T 43282.1-2023  Plastics—Determination of the aerobic biodegradation of plastic materials exposed to seawater—Part 1: Method by analysis of evolved carbon dioxide (English Version)
Standard No.GB/T 43282.1-2023
Statusvalid
LanguageEnglish
File FormatPDF
Word Count10500 words
Price(USD)315.0
Implemented on2024-6-1
Deliveryvia email in 1~3 business day
Detail of GB/T 43282.1-2023
Standard No.
GB/T 43282.1-2023
English Name
Plastics—Determination of the aerobic biodegradation of plastic materials exposed to seawater—Part 1: Method by analysis of evolved carbon dioxide
Chinese Name
塑料 暴露于海水中塑料材料需氧生物分解的测定 第1部分:采用分析释放二氧化碳的方法
Chinese Classification
G31
Professional Classification
GB
ICS Classification
Issued by
SAMR; SAC
Issued on
2023-11-27
Implemented on
2024-6-1
Status
valid
Superseded by
Superseded on
Abolished on
Superseding
Language
English
File Format
PDF
Word Count
10500 words
Price(USD)
315.0
Keywords
GB/T 43282.1-2023, GB 43282.1-2023, GBT 43282.1-2023, GB/T43282.1-2023, GB/T 43282.1, GB/T43282.1, GB43282.1-2023, GB 43282.1, GB43282.1, GBT43282.1-2023, GBT 43282.1, GBT43282.1
Introduction of GB/T 43282.1-2023
GB/T 43282.1-2023 Plastics - Determination of the aerobic biodegradation of plastic materials exposed to seawater - Part 1: Method by analysis of evolved carbon dioxide 1 Scope This document specifies a laboratory test method for determining the degree and rate of the aerobic biodegradation level of plastic materials. Biodegradation is determined by measuring the CO2 evolved from plastic materials when exposed to seawater sampled from coastal areas under laboratory conditions. The conditions described in this document might not always correspond to the optimum conditions for the maximum degree of biodegradation, however this test method is designed to give an indication of the potential biodegradability of plastic materials. Note: This document addresses plastic materials but can also be used for other materials. 2 Normative references The following documents are referred to in the text in such a way that some or all of their content constitutes requirements of this document. For dated references, only the edition cited applies. For undated references, the latest edition of the referenced document (including any amendments) applies. ISO 5667-3 Water quality - Sampling - Part 3: Preservation and handling of water samples ISO 8245 Water quality - Guidelines for the determination of total organic carbon (TOC) and dissolved organic carbon (DOC) ISO 10210 Plastics - Methods for the preparation of samples for biodegradation testing of plastic materials ISO 10523 Water quality - Determination of pH ISO 11261 Soil quality - Determination of total nitrogen - Modified Kjeldahl method 3 Terms and definitions For the purposes of this document, the following terms and definitions apply. 3.1 pelagic zone water body above the seafloor Note 1: It is also referred to as the open water or the water column. Note 2: The surface of the pelagic zone is moved by wind-driven waves, is in contact with the atmosphere and exposed to sunlight. With increasing depth pressure increases, temperature decreases, and light and surface wave energy are attenuated. [SOURCE: ISO 22766:2020, 3.4] 3.2 dissolved inorganic carbon; DIC part of the inorganic carbon in water which cannot be removed by specified phase separation Note: Phase separation can be achieved for example by centrifugation at 40000 m/s−2 for 15 min or by membrane filtration using membranes with pores of 0.2 μm to 0.45 μm diameter. [SOURCE: ISO 14852:2021, 3.4] 3.3 theoretical amount of evolved carbon dioxide; ThCO2 maximum theoretical amount of carbon dioxide evolved after completely oxidizing a chemical compound, calculated from the molecular formula Note: It is expressed as milligrams of carbon dioxide evolved per milligram or gram of test compound. [SOURCE: ISO 14852:2021, 3.5] 3.4 total organic carbon; TOC amount of carbon bound in an organic compound Notey: It is expressed as milligrams of carbon per 100 mg of the compound. [SOURCE: GB/T 40611-2021, 3.14] 3.5 dissolved organic carbon; DOC part of the organic carbon in water which cannot be removed by specified phase separation Note: Phase separation can be achieved for example by centrifugation at 40000 m/s−2 for 15 min or by membrane filtration using membranes with pores of 0.2 μm to 0.45 μm diameter. [SOURCE: ISO 14852:2021, 3.7] 3.6 lag phase time from the start of a test until adaptation and/or selection of the degrading microorganisms is achieved and the degree of biodegradation of a chemical compound or organic matter has increased to about 10 % of the maximum level of biodegradation (3.8) Note: It is measured in days. [SOURCE: ISO 14852:2021, 3.8] 3.7 biodegradation phase time from the end of the lag phase (3.6) of a test until the plateau phase has been reached Note: It is measured in days. [SOURCE: ISO 14852:2021, 3.10] 3.8 maximum level of biodegradation degree of biodegradation of a chemical compound or organic matter in a test, above which no further biodegradation takes place during the test Note: It is measured in per cent. [SOURCE: ISO 14852:2021, 3.9] 3.9 plateau phase time from the end of the biodegradation phase (3.7) until the end of a test Note: It is measured in days. [SOURCE: ISO 14852:2021, 3.11] 3.10 pre-conditioning pre-incubation of an inoculum under the conditions of the subsequent test in the absence of the chemical compound or organic matter under test, with the aim of improving the test by acclimatization of the microorganisms to the test conditions [SOURCE: ISO 14852:2021, 3.13] 4 Principle This document describes two variations of a test method for determining the biodegradability of plastic materials by the indigenous population of microorganisms in natural seawater using a static aqueous test system. The test is performed under mesophilic test conditions for up to two years by incubating plastic materials with either seawater only (“pelagic seawater test”) or with seawater to which low amount of sediment has been added (“suspended sediment seawater test”), coming from the same site as that from which the seawater was taken. Biodegradation is followed by measuring the evolution of carbon dioxide using a suitable, analytical method. The level of biodegradation is determined by comparing the amount of carbon dioxide evolved with the theoretical amount [theoretical amount of evolved carbon dioxide (ThCO2)] and expressed in percentage. The test result is the maximum level of biodegradation, determined from the plateau phase of the biodegradation curve. The principle of a system for measuring evolved carbon dioxide is given in ISO 14852:2021, Annex A.
Contents of GB/T 43282.1-2023
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Keywords:
GB/T 43282.1-2023, GB 43282.1-2023, GBT 43282.1-2023, GB/T43282.1-2023, GB/T 43282.1, GB/T43282.1, GB43282.1-2023, GB 43282.1, GB43282.1, GBT43282.1-2023, GBT 43282.1, GBT43282.1