A Comprehensive Comparison of Physical and Chemical Recycling Pathways
From molecular chains to industrial applications — technical principles, commercialization status, and selection guidance
JIANGSU LIANHENG MACHINERY CO., Ltd. | July 2026
Introduction: Is Chemical Recycling Harder Than Physical Recycling?
1. Physical Recycling: Mechanical Processing & Solid-State Polycondensation
SSP: Molecular Weight “Repair Surgery”
Limitations of Physical Recycling
2. Chemical Recycling: Four Depolymerization Pathways
Four Chemical Depolymerization Routes
3. Why Is Chemical Recycling Harder? Three Core Challenges
4. “Harder” Doesn’t Mean “Shouldn’t Be Done” — Future Outlook
5. Frequently Asked Questions (FAQ)
Q1: Is chemical recycling really harder than physical recycling?
Q2: Can physically recycled PET achieve bottle-grade IV?
Q3: Which of the four chemical routes has been commercialized?
Q4: Can PET be physically recycled infinitely?
Introduction: Is Chemical Recycling Harder Than Physical Recycling?
PET (polyethylene terephthalate) recycling sits at the crossroads of global environmental concerns and significant commercial opportunity. Demand for recycled PET (rPET) continues to grow across bottles, packaging, and fiber applications. Currently, mechanical recycling (physical recycling) technology is highly mature, while emerging chemical recycling technologies rely on depolymerization pathways to break polymer chains back into monomeric building blocks.
A recent question arose: Is chemical recycling harder than physical recycling? This seemingly simple question touches the most critical technological fork in the PET recycling industry chain. This article dissects both pathways at the molecular level to provide an evidence-based answer.

Figure 1: The complete PET bottle recycling process — from collection to end products (Source: ieltsfever.org)
1. Physical Recycling: Mechanical Processing & Solid-State Polycondensation
The logic of physical recycling is straightforward: PET is a thermoplastic polymer that can be remolded above its melting point without breaking molecular chains.
“Mechanical recycling, comprising washing, sorting and extrusion, is a well-established technology and market for bottle to fibre recycling.”
—— Modern Polyesters, Ch. 2 §2.8 (J. Scheirs & T. E. Long, Wiley, 2003)

Figure 2: Industrial PET recycling production line with sorting, crushing, washing, and pelletizing stages
Standard Three-Step Process
- Sorting & Shredding — Remove caps (HDPE/PP) and labels (PVC/paper), grind to 6-14mm flakes
- Deep Washing — Hot alkaline solution with friction washing to remove label glue, residual beverages, and contaminants
- Melt Pelletizing — Flakes are melt-extruded, strand-cut, and pelletized into rPET pellets
SSP: Molecular Weight “Repair Surgery”
PET inevitably degrades during melt processing — hydrolysis, thermal degradation, and thermo-oxidative degradation break molecular chains, reducing intrinsic viscosity (IV). Recycled PET typically has an IV of 0.60-0.75 dL/g, while bottle-grade PET requires 0.80 dL/g or above.
🔬 Solid-State Polycondensation (SSP) Principle: PET pellets are heated above Tg (65-85°C) but below melting point (~265°C), allowing chain ends to continue condensing in the solid state, releasing ethylene glycol and water, and increasing IV. The mature Buhler bottle-to-bottle process combines vacuum extrusion (melt phase) with continuous SSP (solid phase). rPET processed through this route has acetaldehyde content even lower than virgin PET.
Limitations of Physical Recycling
Physical recycling essentially “repairs” rather than “restarts” molecular chains. It cannot completely remove impurities and has limited decontamination capability.
“Due to the required high decontamination levels of recycled PET for food-packaging applications, bottle to bottle recycling should be a chemical recycling process comprising chain degradation and re-polycondensation.”
—— Modern Polyesters, Ch. 2 §2.8
Moreover, each pass through high temperature causes chain degradation. After approximately 3-5 processing cycles, PET’s mechanical properties and thermal stability decline significantly — physical recycling cannot achieve infinite cycling.
2. Chemical Recycling: Four Depolymerization Pathways
The logic of chemical recycling is equally elegant: since PET is polymerized from monomers, depolymerizing back to monomers, purifying, and re-polymerizing achieves true “starting from scratch” recycling.
“The chain degradation can be performed either by hydrolysis, glycolysis, methanolysis or saponification, thus forming monomers and/or oligomers.”
—— Modern Polyesters, Ch. 2 §2.8

Figure 3: Chemical depolymerization of PET to TPA via ball milling and vapor-assisted aging (Source: ChemistryViews)
Four Chemical Depolymerization Routes
| Route | Reactant | Products | Commercialization Status |
| Hydrolysis | H₂O | TPA + EG | ❌ Never commercialized; TPA purification extremely difficult |
| Glycolysis | EG | BHET + oligomers | ✅ Goodyear (1992), Eastman (1997) FDA-approved; niche market |
| Methanolysis | CH₃OH | DMT + EG | ⚠️ DuPont 1996 commercialization; most plants shut down |
| Saponification | NaOH | TPA sodium salt + EG | ❌ Lowest industrialization; saline wastewater issues |
Key challenges by route: • Hydrolysis: Requires strong acid/high temperature and pressure; TPA purification extremely difficult • Glycolysis: BHET purification is the core bottleneck, but products can be directly re-polymerized • Methanolysis: DMT can be purified by distillation, but recycled monomer cost always exceeds virgin monomer • Saponification: Saline wastewater treatment costs are high; worst economic viability
3. Why Is Chemical Recycling Harder? Three Core Challenges
| 🔄 Mass Transfer Bottleneck Reactants (EG, methanol, or water) are polar small molecules; PET melt is weakly polar and highly viscous — the two phases are nearly immiscible, creating enormous mass transfer resistance. | 💰 Purification Cost DMT and EG form an azeotrope requiring special distillation. Co-products have vapor pressures close to DMT, making separation nearly impossible. | 📉 Historical Evidence Four major US chemical companies — Eastman Kodak, Hoechst-Celanese, DuPont, Goodyear — all obtained FDA approval but most shut down in the 1990s. |
4. “Harder” Doesn’t Mean “Shouldn’t Be Done” — Future Outlook
Physical recycling has its cycling ceiling, while chemical recycling breaks through it — returning to monomer-level recycling theoretically enables infinite cycling.
💡 Key Conclusions
Physical and chemical recycling are not competing approaches — they are complementary pathways:
- Physical Recycling — Mature technology, cost-controllable, already addressing 80% of market demand (“bottle-to-fiber”). SSP advancement also enables bottle-to-bottle recycling.
- Chemical Recycling — High barriers, high costs — mass transfer is the bottleneck, purification is the cost driver, and the economic equation has remained unbalanced for 30 years. But the ceiling is higher, enabling true “infinite cycling.”
Schade et al. (2024) note that chemical recycling is entering a new wave of innovation, with novel catalyst systems, reactor designs, and process integration solutions narrowing the cost gap with mechanical recycling.
Answering the question: Chemical recycling is harder — harder in mass transfer, harder in purification, harder in economics. But this is merely a longer road, not a dead end.
5. Frequently Asked Questions (FAQ)
Q1: Is chemical recycling really harder than physical recycling?
Yes. Chemical recycling faces three core challenges: mass transfer bottleneck (polar small molecules immiscible with high-viscosity PET melt), high purification costs (DMT-EG azeotrope difficult to separate), and poor economics (recycled monomer cost exceeds virgin monomer). Four major US chemical companies commercialized but most shut down. However, chemical recycling enables true infinite cycling with a higher ceiling.
Q2: Can physically recycled PET achieve bottle-grade IV?
Yes. Recycled PET IV is typically 0.60-0.75 dL/g. Through SSP (Solid-State Polycondensation), IV can be raised above 0.80 dL/g, meeting bottle-grade standards. The Buhler bottle-to-bottle process combining vacuum extrusion and continuous SSP produces rPET with acetaldehyde content even lower than virgin PET.
Q3: Which of the four chemical routes has been commercialized?
Glycolysis is the only route surviving in niche markets. Goodyear (1992) and Eastman (1997) received FDA approval. Methanolysis was commercialized by DuPont in 1996 but most plants have shut down. Hydrolysis has never been commercialized, and saponification has the lowest level of industrialization.
Q4: Can PET be physically recycled infinitely?
No. Each melt processing cycle causes molecular chain degradation. After approximately 3-5 processing cycles, PET’s mechanical properties and thermal stability decline significantly. Chemical recycling, returning to monomer level, theoretically enables infinite cycling.
6. Glossary
| English Term | 中文术语 |
| mechanical recycling | 机械回收 / 物理再生 |
| chemical recycling | 化学回收 / 化学再生 |
| solid-state polycondensation (SSP) | 固相缩聚 |
| depolymerization | 解聚 |
| glycolysis | 醇解 |
| methanolysis | 甲醇解 |
| hydrolysis | 水解 |
| saponification | 皂化 |
| intrinsic viscosity (IV) | 特性粘度 |
| bottle-to-bottle recycling | 瓶到瓶回收(闭环) |
| bottle-to-fibre recycling | 瓶到纤维回收(开环) |
| mass transfer | 传质 |
| BHET | 对苯甲酸双羟乙酯 |
| DMT | 对苯甲酸二甲酯 |
| TPA | 对苯甲酸 |
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