May 25, 2025 · by Tidey Ocean Foundation · updated June 11, 2026
8 Alternatives to Plastic: What They Are, Where They Stand in 2025, and What Honest Progress Looks Like
PLA, PHA, mycelium, seaweed, and four other materials aim to replace petroleum plastic. Here is a realistic assessment of where each one stands.

The search for materials that perform like plastic without persisting in the environment the way plastic does has accelerated significantly over the past decade, as regulatory pressure, consumer demand, and investor interest have converged. Eight categories of alternatives have emerged as the most technically developed, and each has real strengths alongside real constraints that are frequently understated in public discussions about them.
One framing note before reviewing any of them: global plastic production reached 430 million metric tonnes in 2024 and is projected by the OECD to continue rising. Even optimistic scaling scenarios for the alternatives below would replace a small fraction of that volume within a decade. This is not a reason to dismiss alternative materials; it is a reason to be clear that alternatives alone cannot resolve the plastic pollution problem. They are one lever among several, alongside production reduction, extended producer responsibility policy, and collection infrastructure. A material that biodegrades is only better than conventional plastic if it actually biodegrades in the conditions where it ends up, and if the energy and agricultural inputs required to produce it are genuinely lower than the petroleum-based alternative it replaces.
Polylactic acid, or PLA, is produced by fermenting plant starches, most commonly corn or sugarcane, and is the most commercially available bioplastic today. PLA is transparent, rigid, and used in food packaging, single-use cutlery, and cups. Its biodegradation claim requires a specific condition: industrial composting at 55 to 60 degrees Celsius, sustained for several weeks. In a home compost pile, a landfill, or the ocean, PLA does not biodegrade within any practical timeframe. PLA also poses a contamination risk for conventional plastic recycling: it looks nearly identical to PET under visible light and, if mixed with PET in a recycling stream, contaminates the recovered material and reduces its value. Some industrial composting facilities in the EU and US accept PLA; many do not. The honest assessment of PLA: conditionally better than conventional plastic if adequate industrial composting infrastructure exists for it, which it currently does not in most markets.
Polyhydroxyalkanoates, known as PHA, are produced by bacterial fermentation and represent the most environmentally promising category on this list. Unlike PLA, PHA biodegrades in soil, seawater, and freshwater, meaning it does not require specific industrial conditions for end-of-life. It breaks down in marine environments within months, making it potentially valuable for applications where ocean entry is a real risk. Commercial production is growing: companies including Danimer Scientific and RWDC Industries produce PHA for packaging and service ware. The constraint is cost: PHA typically runs two to five times the price per kilogram of conventional plastic, and production capacity remains orders of magnitude below what substituting even packaging plastics would require. PHA has the best environmental profile of any material on this list; it is not yet at cost parity.
Seaweed and algae-based materials are produced by processing cultivated or harvested marine biomass into flexible films, rigid packaging, and coatings. Companies including Notpla in the UK, Sway in the US, and Evoware in Indonesia have developed commercial products in this category. Seaweed grows rapidly without freshwater, fertilizers, or arable land, and can produce biomass at rates that exceed terrestrial crops substantially. Some seaweed-based formulations are edible and fully compostable at home or in industrial settings. The scaling constraints are real: global seaweed aquaculture production would need to expand dramatically to supply packaging applications at commercial volumes, and the processing chemistry for some applications remains proprietary and expensive. This is the category most worth watching for the next decade.
Chitosan, derived from chitin in crustacean shells and fish scales, provides natural antimicrobial properties useful for food packaging and medical applications. It uses seafood processing waste that would otherwise be discarded, making its feedstock genuinely low-value. Its biodegradation is real and occurs without specialized conditions. The scalability constraint is feedstock: chitosan production is bounded by the volume of seafood processing waste generated globally, which is not sufficient to substitute for significant plastic volumes. Chitosan is most useful for high-value, low-volume applications, including pharmaceutical packaging and wound dressings, rather than commodity packaging.
Molded fiber, produced from recycled paper pulp and natural fibers, is already commercially widespread in egg cartons, electronics cushioning, and medical device trays. It requires no new technology, uses existing recycling infrastructure, and biodegrades readily. Its limitations are water resistance and structural flexibility: molded fiber does not perform well for liquid contact without additional coatings, which may be plastic-based and negate part of the benefit. The material has already displaced polystyrene in many electronics packaging applications and continues to expand in that direction.
Bacterial cellulose, produced by certain bacteria as ultrafine nanofibers, creates films and coatings with good strength and flexibility. It is at an earlier commercial stage than the materials above: production costs are high, and current applications are concentrated in specialty medical and electronics uses rather than commodity packaging. As production processes improve, bacterial cellulose may become relevant for food packaging and barrier applications, but it is not near commodity scale today.
Arboform, sometimes called liquid wood, is a thermoplastic made from lignin, a byproduct of paper manufacturing. It can be injection-molded into rigid shapes and substitutes for some conventional plastics in consumer goods like toys and small household items. Its biodegradation is conditional on industrial composting conditions similar to PLA. It is available commercially in Europe for specific product categories but remains a niche material constrained by its brittleness and cost compared to standard thermoplastics.
Mycelium, grown from fungal root structures on agricultural waste, can be molded into custom packaging shapes that substitute for polystyrene foam. Companies including Ecovative in the US and Grown Bio in the Netherlands sell commercial products used in electronics and consumer goods packaging. Mycelium packaging is fully compostable at home, carbon-neutral in production, and flame-resistant. The production timeline, days to weeks rather than hours, and current cost premium over polystyrene foam are the main constraints on scaling, but the cost gap has narrowed significantly in recent years.
What these eight alternatives share is that they address the end-of-life problem rather than the production volume problem. If every unit of plastic produced today were replaced with a biodegradable alternative tomorrow, the 170 trillion plastic particles estimated to float at the ocean surface would remain there, fragmenting further, for decades. New materials that biodegrade faster help prevent future accumulation; they do not clean up what is already there. Production reduction, collection infrastructure, and alternatives all matter as simultaneous interventions, not sequential ones.
What is the difference between biodegradable and compostable on packaging labels?
Biodegradable means the material will break down by biological processes under some conditions but does not specify how long, in what environment, or into what byproducts. Compostable is a more specific claim: material certified to EN 13432 or ASTM D6400 will break down in industrial composting within six months. Neither term means the material will degrade if it reaches the ocean or a landfill, where conditions differ substantially from industrial composting. Some biodegradable plastics take decades to break down in landfills and may not degrade meaningfully in marine environments at all.
Why does PLA contaminate PET recycling?
PLA and PET are both clear, rigid polyesters that look nearly identical under visible light. Sorting performance varies by facility and equipment; PLA can be misidentified or missed in mixed recycling streams, creating a contamination risk for PET recycling. PLA melts at a lower temperature than PET, so when mixed PLA-contaminated PET is processed, the PLA degrades and forms streaks or weaknesses in the recycled material, reducing its quality and market value. As PLA use in food service grows, contamination of PET recycling streams has become a documented problem at facilities that receive commingled plastics.
Sources
- UNEP. Plastic Pollution and Marine Litter. https://www.unep.org/topics/ocean-seas-and-coasts/ecosystem-degradation-pollution/plastic-pollution-and-marine-litter
- European Bioplastics. Bioplastics market data and standards resources. https://www.european-bioplastics.org/market/
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