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Which Is More Environmentally Friendly for White Paper Cup Linings: PE or PLA?
author: Iris
2025-11-26
I. Introduction
With increasingly severe global environmental problems, the sustainability of single-use packaging materials has become a focus of attention. As a widely used packaging container in daily life, the environmental performance of the inner wall coating material of white paper cups directly affects the overall environmental performance of the product. Currently, two main materials are used for the inner wall of white paper cups: PE (polyethylene) and PLA (polylactic acid). PE is a petroleum-based thermoplastic polymer with excellent moisture-proof properties, but it is difficult to degrade in the environment; PLA is a bio-based thermoplastic polymer made from renewable resources such as corn, and theoretically, it is biodegradable.
As the world's largest economy and one of the largest consumers of plastic products, the United States has a significant influence on the development of global packaging materials through its environmental standards system. The US environmental standards system covers multiple levels, including federal, state, and local standards, such as the EPA (Environmental Protection Agency) environmental standards, the FDA (Food and Drug Administration) food contact material specifications, and ASTM (American Society for Testing and Materials) technical standards. In particular, the EPA's National Plastics Pollution Prevention Strategy, released in 2024, and recent regulations such as California's SB 54, have placed higher demands on the environmental performance of packaging materials.
However, the comparison of the environmental performance of PE and PLA materials in white paper cup applications remains controversial. On the one hand, PLA is considered an ideal alternative to traditional plastics, possessing biodegradability and renewability; on the other hand, PLA production requires a large amount of agricultural land, and its degradation requires specific industrial composting conditions.
II. Comparison of Basic Material Properties
2.1 PE Material Properties
Polyethylene (PE) is a thermoplastic polymer polymerized from ethylene monomers. Based on density and structure, it can be divided into low-density polyethylene (LDPE), linear low-density polyethylene (LLDPE), and high-density polyethylene (HDPE). PE materials possess the following characteristics:
In terms of physical properties, PE exhibits excellent moisture resistance and gas barrier properties, with a tensile strength between 50-80 MPa. PE has a relatively high melting point, making it suitable for applications over a wide temperature range. These properties make PE an ideal choice for paper serving cups coatings, effectively preventing liquid leakage.
In terms of chemical structure, PE molecules have a non-polar structure, containing no positive or negatively charged groups. The molecules are tightly packed, with no voids within the material, resulting in exceptionally high density. This structural characteristic determines PE's excellent chemical stability, but also makes it difficult to degrade in the natural environment.
In terms of raw material sources, PE primarily uses petroleum as a raw material, with approximately 57% of polyethylene production derived from fossil fuels. Producing one ton of polyethylene requires approximately 1.75 tons of petroleum, generating significant amounts of carbon dioxide and other greenhouse gases. Globally, approximately 99% of plastics come from fossil resources (oil and natural gas), making PE production closely linked to the extraction and refining of fossil fuels.
2.2 PLA Material Characteristics
Polylactic acid (PLA) is a bio-based thermoplastic polyester, primarily produced from renewable resources such as corn and sugarcane through fermentation processes. PLA materials possess the following characteristics:
In terms of physical properties, the tensile strength of PLA is typically between 10-30 MPa, lower than that of PE. The mechanical properties of PLA films are comparable to PET and superior to PS, but its melting point and glass transition temperature are lower than both PET and PS. The glass transition temperature of PLA changes over time, but remains unaffected under humidity levels of 10-95% and storage temperatures of 5-40℃.
In terms of chemical structure, PLA molecular chains contain polar ester bonds, resulting in weak repulsive forces between the chains. Unlike PE, the chains are not tightly packed, and the material contains small voids. This structural characteristic gives PLA a certain degree of hydrophilicity and also facilitates its biodegradability.
In terms of raw material sources, PLA is mainly produced from corn starch through fermentation to produce lactic acid, which is then polymerized. The production process comprises four main stages: sugarcane planting and transportation to the sugar mill, sugarcane conversion to raw sugar, raw sugar fermentation to produce lactic acid, and lactic acid conversion to lactide and PLA. The plants absorb carbon dioxide during their growth, providing PLA with the potential for carbon sequestration.
2.3 Comparison of Food Contact Safety
Under the US FDA regulatory system, both PE and PLA are considered safe food contact materials, but their regulatory pathways differ.
PE materials are widely recognized as safe for food contact. According to FDA regulations, PE coatings must comply with 21 CFR 177.1520, ensuring a migration level ≤0.5% w/w. The FDA has approved various PE materials, including HDPE, LDPE, and LLDPE, for food contact applications.
PLA materials, in their pure form, are designated by the FDA as GRAS (Generally Recognized As Safe) and can be used in food contact applications. However, PLA coatings require FCN (Food Contact Substance Notification) certification. In February 2024, CARBIOS's PLA biodegradable enzyme solution received FDA FCN 2325 certification, allowing its use in food contact packaging materials sold in the United States. This opens up more possibilities for the application of PLA in the food packaging field.
It is worth noting that some bio-based materials certified by EN 13432 (such as PLA) may release acidic substances during degradation. Although they meet composting standards, they may trigger sensitive FDA reviews regarding pH changes, requiring additional stability improvements.
III. Comparison of Post-Use Degradation
3.1 Comparison of Recyclability
Recycling is an important way to achieve a circular economy of materials, but PE and PLA face different challenges in the recycling system.
The current recycling status of PE in the United States is not ideal. According to data from the American Plastics Recycling Association, the current recycling rate of PET, HDPE, and PP plastics in the United States is about 20%. Recyclers estimate that if more material could be obtained, they could double the current overall recycling rate. Specifically regarding PE materials, the recycling rate in North America is approximately 14%, far lower than the 30% in Europe. The national recycling rate for plastic packaging in the United States is only 13.3%, representing the largest environmental gap.
The main challenges facing PE recycling include:
Difficulty in material separation: The PE coating is tightly bonded to paper fibers, requiring specialized repulping processes for separation, which most standard paper mills lack.
Limitations in recycling facilities: Globally, only 26% of municipalities have appropriate systems for collecting and processing coated white paper cups, and pollution from beverage residues reduces recycling efficiency by 32%.
Economic feasibility: The economic benefits of PE recycling are limited, with the price of recycled PE fluctuating significantly, rising from 31 cents/lb to 63 cents/lb.
Limitations in recycling facilities: Globally, only 26% of municipalities have appropriate systems for collecting and processing coated white paper cups, and pollution from beverage residues reduces recycling efficiency by 32%.
Economic feasibility: The economic benefits of PE recycling are limited, with the price of recycled PE fluctuating significantly, rising from 31 cents/lb to 63 cents/lb.
However, recycling PE also has its advantages. Studies show that the production of recycled PE can save approximately 1.5 tons of CO₂ emissions per ton compared to virgin PE. In 2024, the FDA accelerated the approval process for recycled plastics, providing more opportunities for the application of recycled PE in food packaging.
The current state of PLA recycling is more complex. While PLA is theoretically recyclable, it faces numerous difficulties in practice:
Incompatibility with traditional recycling systems: PLA cannot be recycled with conventional paper products because it would contaminate the recycling stream.
Lack of dedicated recycling facilities: Currently, the United States lacks infrastructure specifically for PLA recycling.
Heat recovery limitations: PLA has a low melting point and is easily degraded during recycling, affecting the quality of recycled products.
Lack of dedicated recycling facilities: Currently, the United States lacks infrastructure specifically for PLA recycling.
Heat recovery limitations: PLA has a low melting point and is easily degraded during recycling, affecting the quality of recycled products.
Therefore, PLA recycling primarily relies on chemical recycling pathways, such as hydrolysis or alcoholysis processes, but these technologies are not yet widely commercially available.
3.2 Compostability Comparison
Compostability is a major advantage of PLA materials, but it requires specific conditions to achieve.
The compostability of PLA has been verified by multiple standards. According to ASTM D6400 standards, PLA exhibits excellent performance under industrial composting conditions (50-60℃, >58℃):
Degradation time: Complete degradation in 45-60 days
Degradation rate: 65%-80% degradation within 80-180 days
Degradation conditions: Requires temperature > 50-60℃, relative humidity > 70%, pH 5.5-8.0
Degradation rate: 65%-80% degradation within 80-180 days
Degradation conditions: Requires temperature > 50-60℃, relative humidity > 70%, pH 5.5-8.0
The primary degradation mechanism of PLA is hydrolysis, a non-biological process occurring in the presence of moisture. In the high-temperature environment of industrial composting facilities, hydrolysis and subsequent biodegradation occur rapidly. Studies show that PLA ultimately degrades into CO₂ and H₂O, which can then be converted into starch—a raw material for lactic acid—through photosynthesis, forming a natural cycle.
However, PLA's compostability also has limitations: Difficult for home composting: Most PLA materials are unsuitable for home composting, especially those specifically designed for industrial composting. Strict temperature requirements: Home composting typically involves low temperatures and unstable conditions, resulting in extremely slow PLA degradation under these conditions. High facility dependence: Effective PLA degradation is highly dependent on the presence of industrial composting facilities.
PE's compostability is almost zero. PE does not biodegrade under composting conditions; its nonpolar molecular structure makes it extremely difficult to decompose in the natural environment. Even under the high temperatures of industrial composting, PE does not undergo significant degradation.
3.3 Comparison of Natural Environment Degradation
The degradation behavior of materials in the natural environment directly relates to their long-term environmental impact.
PE degrades extremely slowly in the natural environment. Studies have shown that in marine environments, PE takes hundreds of years to degrade.
After 10 years, one-third of the original material disappears; after 30 years, nearly two-thirds become microplastics; and after 100 years, a small portion remains intact.
Under simulated marine conditions in the laboratory, the degradation half-life of PE film under UV irradiation at 300 W/m² is approximately 180 days. However, in natural marine environments, the degradation rate is limited by the depth of UV penetration, typically taking months to years.
In seawater, brackish water, and freshwater environments, PE degrades relatively faster in seawater, but overall, the degradation is still slow.
The degradation of PE in natural environments mainly occurs through photo-oxidation and mechanical abrasion processes, leading to microplastic pollution. These microplastics cause serious harm to the environment and organisms, including physical damage, chemical toxicity, and bioaccumulation.
PLA degradation in natural environments exhibits significant environmental dependence:
Soil environment: Studies have found that in soils of the Midwestern United States, molded PLA rods show minimal degradation after one year.
Aquatic environment: PLA exhibits poor biodegradation rates in aquatic ecosystems.
Special environments: In certain special environments, such as water bodies containing cyanobacteria, daytime photosynthesis raises the pH to 11, causing PLA to become significantly brittle, indicating a substantial decrease in molecular weight.
Aquatic environment: PLA exhibits poor biodegradation rates in aquatic ecosystems.
Special environments: In certain special environments, such as water bodies containing cyanobacteria, daytime photosynthesis raises the pH to 11, causing PLA to become significantly brittle, indicating a substantial decrease in molecular weight.
The slow degradation of PLA in natural environments is primarily due to the lack of high temperature, high humidity, and microbial conditions required for industrial composting. However, studies also indicate that PLA does not contribute to persistent microplastic pollution because its hydrolysis process inhibits microplastic formation.
3.4 Current Status of Composting Infrastructure in the United States
The distribution of composting infrastructure in the United States is severely inadequate, directly impacting the realization of the environmental benefits of PLA materials.
According to the latest data, the United States currently has approximately 200 commercial composting facilities processing food waste, and another approximately 2,700 facilities processing only yard waste. The distribution of these facilities shows significant regional differences:
Northeast: Many facilities with small or micro-design capabilities
Southeast and Pacific Region: Fewer facilities but larger processing capacities, leading in terms of tonnage processed.
Southeast and Pacific Region: Fewer facilities but larger processing capacities, leading in terms of tonnage processed.
It is worth noting that many facilities processing only yard waste have the potential to be converted to accept and process food waste. For example, Colorado opened its first Class 1 commercial composting facility in November 2024, increasing its composting capacity tenfold.
However, the existing composting infrastructure is far from meeting the demand. Taking New York City as an example, a bill proposed by the City Council requires each borough to have at least 180,000 tons/year of aerobic processing capacity by 2024, totaling 900,000 tons/year citywide, but current facility capacity is far from meeting this goal.
This lack of infrastructure poses a significant challenge to the application of PLA materials. Even though PLA has excellent compostability, its environmental advantages cannot be realized without corresponding processing facilities. In contrast, while PE is non-biodegradable, it can be processed through existing recycling systems (albeit inefficiently).
Ⅳ. Results
Under the current US environmental standards framework, PLA materials have a significant advantage in environmental performance.
In terms of environmental impact during production processes, PLA's carbon footprint is 45%-85% lower than PE, energy consumption is reduced by 40%-60%, and it does not cause ecological damage to the petrochemical industry. While PLA production requires agricultural land and water resources, its carbon cycle advantages and positive soil impacts largely offset these negative effects.
Regarding post-use degradation, PLA degrades completely within 45-60 days under industrial composting conditions without creating persistent microplastic pollution. In contrast, PE takes hundreds of years to degrade and produces severe microplastic pollution. Although PE has certain advantages in existing recycling systems, its 14% recycling rate is far from sufficient to address environmental issues.
PLA demonstrates significant advantages in its impact on ecosystems and biodiversity. PE's microplastic pollution poses serious harm to aquatic and terrestrial organisms, while PLA does not form microplastics and has a positive effect on soil ecosystems. In terms of carbon cycling, PLA can achieve a closed-loop cycle, possessing the potential for carbon neutrality or even negative emissions.
However, the full realization of PLA's environmental advantages largely depends on the progress of composting infrastructure development in the United States. Currently, the US only has 200 commercial composting facilities processing food waste, far from meeting the demand. Therefore, it is recommended that the US government accelerate the construction of composting infrastructure, improve the PLA recycling system, strengthen standard setting and certification, promote industrial transformation, and enhance public education.
In summary, although PLA still has shortcomings in some aspects (such as recyclability and heat resistance), its overall environmental advantages make it an ideal choice for paper hot cup coating materials. With technological advancements and improved infrastructure, PLA is expected to become an important solution to the plastic pollution problem and make a significant contribution to achieving sustainable development goals.
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