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ASTM D6002-96 (Reapproved 2002) provides a comprehensive framework for assessing the compostability of environmentally degradable plastics. As a Standard Guide, it establishes suggested criteria, procedures, and a general approach rather than a rigid specification. The scope explicitly covers the development of a testing regimen to demonstrate that a plastic material is compostable.
Central to the guide are the formal definitions drawn from Terminology D 883. A biodegradable plastic is defined as a degradable plastic in which the degradation results from the action of naturally occurring microorganisms such as bacteria, fungi, and algae. More specifically, a plastic is considered compostable if it is capable of undergoing biological decomposition in a compost site as part of an available program, such that the material is not visually distinguishable and breaks down into carbon dioxide, water, inorganic compounds, and biomass, at a rate consistent with known compostable materials.
The guide recommends a tiered analytical approach that does not create new tests but rather assembles a battery of existing ASTM standards and OECD guidelines. The primary parameters measured include aerobic biodegradation, physical disintegration during composting, and the quality of the final compost residuals.
| 🟦 Assessment Category | 📏 Standard Method | 🎯 Key Measured Parameter |
|---|---|---|
| Aerobic Biodegradation | D 5338 | Conversion of carbon to CO₂ under controlled composting |
| Aerobic Biodegradation | D 5988 / D 5209 | Biodegradation rate in soil and municipal sludge environments |
| Disintegration / Compost Exposure | D 5509 / D 5512 | Visual resolution and physical breakdown in simulated compost |
| Residual Solids Preparation | D 5951 / D 5152 | Water extraction and preparation for ecotoxicity testing |
| Ecotoxicity (Aquatic) | E 1440 | Acute toxicity to rotifer Brachionus (LC50) |
| Ecotoxicity (Terrestrial) | OECD 207 / 208 | Earthworm mortality and plant germination inhibition |
A defining aspect of the D6002 guide is the emphasis on the environmental safety of the final compost product. The residual solids obtained from biodegradation studies must undergo specific evaluations to ensure the degradation process does not yield toxic byproducts. The guide explicitly links to OECD terrestrial plant and earthworm testing guidelines for a comprehensive risk assessment.
| 🔬 Compartments Assessed | 📋 Test Guideline | ⚡ Endpoint |
|---|---|---|
| Soil Fauna | OECD Guideline 207 | Earthworm (Eisenia foetida) acute toxicity |
| Terrestrial Flora | OECD Guideline 208 | Terrestrial plant seedling emergence and growth |
| Waste Feedstock Quality | ORCA Document | Evaluation of feedstock for source-separated biowaste composting |
Biodegradable refers to degradation by naturally occurring microorganisms. Compostable is stricter and requires the plastic to break down in a compost site, become not visually distinguishable, convert to CO₂, water, and biomass, and do so at a rate consistent with known compostable materials.
The guide relies heavily on ASTM D 5338 (Test Method for Determining Aerobic Biodegradation of Plastic Materials Under Controlled Composting Conditions). This is the core method for measuring the percentage of organic carbon converted to carbon dioxide in a composting environment.
The guide mandates evaluating the residual solids prepared via ASTM D 5951. Acute ecotoxicity is then assessed using ASTM E 1440 (aquatic rotifer) and OECD Guidelines 207 and 208, which respectively measure earthworm survival and terrestrial plant germination/growth inhibition.
No. D6002 is explicitly categorized as a Standard Guide. It provides a general approach and selection of criteria rather than passing/failing thresholds. According to its scope, it must be used in conjunction with the specific test methods and practices it references. There is no equivalent ISO standard (see Note 1).