| HS Code | 790817 |
| Biobasedcontent | 40% |
| Materialtype | Polylactic Acid (PLA) based biopolymer |
| Density | 1.24 g/cm³ |
| Meltflowrate | 3-5 g/10 min at 190°C/2.16 kg |
| Meltingtemperature | 150 °C |
| Glasstransitiontemperature | 55-60 °C |
| Tensilestrengthatbreak | 25-35 MPa |
| Tensilemodulus | 300-500 MPa |
| Elongationatbreak | 300-400% |
| Tearresistance | 50-70 N/mm |
| Filmthicknessrange | 15-50 µm |
| Processingmethod | Blown film extrusion, cast film extrusion |
| Compostability | Compostable according to EN 13432 |
| Foodcontact | Suitable for food contact (EU 10/2011) |
| Transparency | High transparency |
As an accredited INZEA F11 Flexible 40% Bio-Based Film Polylactic Acid factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | INZEA F11 Flexible 40% Bio-Based Film Polylactic Acid is packaged in 25 kg moisture-barrier bags, palletized and wrapped for transport. |
| Container Loading (20′ FCL) | 20′ FCL loaded with palletized 25 kg bags of INZEA F11 bio-based PLA film resin, shrink-wrapped and secured for export. |
| Shipping | INZEA F11 Flexible 40% Bio-Based Film Polylactic Acid is shipped in moisture-barrier rolls or sheets, palletized and stretch-wrapped. It is not regulated as dangerous goods. Keep dry, cool, and away from direct sunlight/heat. Follow SDS handling and local transport regulations. Include batch, quantity, and safety documentation. |
| Storage | Store INZEA F11 Flexible 40% Bio-Based Film Polylactic Acid in a cool, dry, well-ventilated area away from direct sunlight, heat, ignition sources, and moisture. Keep material in sealed original packaging, palletized off the floor, and avoid excessive stacking or mechanical stress. Protect from UV, humidity, and incompatible chemicals. Maintain recommended storage temperature, typically below 30°C, and use FIFO stock rotation. |
| Shelf Life | Typically 12 months from production when stored unopened in original packaging, cool, dry, away from moisture and direct sunlight. |
When run on blown-film lines, INZEA F11 Flexible, a 40% bio-based film-grade polylactic acid compound, sits within a melt-temperature corridor of 165–185 °C at the adapter and die; below 160 °C, residual crystallites from incomplete melting yield die-lip deposits, while sustained residence above 190 °C initiates chain scission that collapses bubble stability. The converter uses the compound at 100 wt% as the primary feed for monolayer compostable retail carrier bags. Where dart impact tested under ASTM D1709-16a falls below 150 g on films below 20 µm, a second screw feeder meters polybutylene adipate terephthalate at 10–20 wt%; the PBAT grade is selected with an MFR of 2–5 g/10 min at 190 °C/2.16 kg per ISO 1133-1:2022. Pre-drying at 70–80 °C for 4–6 h in a closed-loop desiccant dryer to below 250 ppm residual moisture is not optional; bag production at 300 ppm moisture shows hydrolysis-driven melt viscosity reduction, increased gels, and gauge variation. The blown-film line uses a 30:1 L/D single-screw extruder with a barrier feed section, a die gap of 1.0–1.4 mm, a blow-up ratio of 2.5:1–3.5:1, and frost-line height of 1.5–2.0 die diameters; on 50–70 mm screws running 80–150 kg/h, bubble oscillation is controlled by twin-lip air rings and internal bubble cooling when layflat exceeds 1,200 mm. The collapsed film is treated to 38–42 mN/m, gusseted, perforated where organic waste caddy liners require breathability, and welded on side-seal bag machines running 45–70 cycles/min. Certification is evaluated under EN 13432:2000, with disintegration test method ISO 16929:2021 and aerobic biodegradation ISO 14855-1:2012; where the film enters North American municipal composting streams, labelling follows ASTM D6400-23. Terminal products are compostable retail carrier bags and kitchen caddy liners.
Soil-biodegradable mulch film conversion begins from a different end-use constraint: the film must remain intact long enough to suppress weeds and retain soil moisture, then fragment and biodegrade in soil without leaving persistent residues. The applicable framework is EN 17033:2018, which requires soil biodegradation testing under ISO 17556:2019, determination of disintegration in field or simulated soil conditions, and eco-toxicity tests on the resulting soil. INZEA F11 Flexible is metered as 100 wt% of the film matrix, with carbon black masterbatch added at 3–5 wt% for light exclusion; converters should not exceed 5 wt% carbon black, because higher filler loadings alter the melt viscosity and can reduce the elongation required for laying over raised beds. The film is extruded on blown-film lines with a die gap of 0.8–1.2 mm, melt temperature 165–180 °C, and blow-up ratio 2.0:1–2.8:1, producing layflat widths of 800–1,600 mm and thicknesses of 12–25 µm; below 15 µm, bubble stability becomes highly sensitive to ambient air movement, and the line is fitted with a double-lip cooling ring plus a collapsing frame that maintains bubble symmetry. The downstream process is slit-to-width winding on surface winders with tension control below 0.1 N/mm to avoid blocking. The terminal products are soil-biodegradable agricultural mulch films for annual horticultural row crops; published degradation rate curves for this exact compound in specific soil types are limited, so the converter must validate achievement of the final soil biodegradation threshold under the intended regional soil temperature and moisture profile.
Fresh produce packaging lines impose a clarity requirement that excludes most impact modifiers, so the film is run as 100 wt% INZEA F11 Flexible with only 1–2 wt% anti-block masterbatch when tight winding on 600–1,200 mm cores is expected. The film is blown at 165–175 °C and then micro-perforated by needle rolls; the perforation density is set at 40–80 holes/m² with hole diameters 0.5–1.0 mm to control oxygen and carbon dioxide transmission for leafy greens, herbs, or citrus. Compliance for compostability is assessed under EN 13432:2000; where direct food contact is intended, the converter must verify that the food-contact statement for the specific grade meets Regulation (EU) No 10/2011 and that overall migration does not exceed the 10 mg/dm² limit under the intended food simulant. On form-fill-seal lines running 40–80 packs/min, the heat-seal jaws are maintained at 95–120 °C with dwell 0.5–1.0 s and jaw pressure 0.3–0.6 MPa; seal strength is checked under ASTM F88/F88M-21 and held above 6 N/25 mm for bag widths up to 350 mm. Downstream conversion includes gusseting, printing on water-based flexo presses, and wicket punching for automated packing. Terminal products are compostable fresh produce bags and flow-wrapped salad packaging.
Because e-commerce mailer films operate at 40–70 µm and must survive repeated edge folding and courier handling, the formulation shifts from monolayer 100 wt% F11 to a modified melt blend. The compostable mailer compound is fed at 80–90 wt% INZEA F11 Flexible with 10–20 wt% PBAT to lift Elmendorf tear strength above 8 N in machine direction and 12 N in transverse direction under ASTM D1922-23. The blown-film line is configured with a die gap of 1.2–1.6 mm, blow-up ratio 2.0:1–2.5:1, and total film thickness 40–70 µm; because heat removal across the thicker gauge limits output, a 70 mm extruder typically runs at 60–100 kg/h on this structure, lower than the throughput of thin retail bag film. Certification is evaluated at the final mailer thickness under EN 13432:2000 and ASTM D6400-23; this is necessary because disintegration time and heavy-metal thresholds are tested on the actual final article, and thin-film data cannot be extrapolated to thick films. The film is slit, flexo-printed, varnished, and converted into self-seal mailers with tear-notch initiation. Terminal products are compostable e-commerce mailers and padded liner bags.
| Downstream scenario | Primary standard | Supporting test method | Operating threshold |
|---|---|---|---|
| Compostable retail carrier bags | EN 13432:2000 | ISO 16929:2021, ISO 14855-1:2012 | Moisture < 250 ppm; melt 165–185 °C |
| Soil-biodegradable mulch film | EN 17033:2018 | ISO 17556:2019 | Thickness 12–25 µm; carbon black 3–5 wt% |
| Fresh produce perforated film | EN 13432:2000 | Regulation (EU) No 10/2011 | Migration < 10 mg/dm²; seal > 6 N/25 mm |
| E-commerce mailer film | EN 13432:2000, ASTM D6400-23 | ASTM D1922-23 | PBAT 10–20 wt%; gauge 40–70 µm |
| Compostable multi-layer pouch sealant web | EN 13432:2000 | ASTM F88/F88M-21 | Sealant layer 12–20% of total gauge |
Coextruded sealant-web use of INZEA F11 Flexible shifts the line from a monolayer die setup to a three-layer blown-film configuration, where the sealant layer is metered as 100 wt% F11 Flexible and occupies 12–20% of the total thickness. The outer skin layers may be PBAT-rich formulations to add puncture resistance, while the core uses the same F11 compound; the total film thickness ranges from 45–70 µm with a die gap of 1.1–1.4 mm. The seal initiation temperature of the F11 layer is measured on a lab sealer according to ASTM F88/F88M-21; converters have documented acceptable seal strength above 6 N/25 mm on the sealant side at jaw temperatures of 95–115 °C and dwell times of 0.5–0.8 s. The entire laminate structure must meet EN 13432:2000 for compostability of packaging waste, and where the pouch is used for dry food contact, the converter must verify compliance under Regulation (EU) No 10/2011 for the food-contact layer. Downstream conversion includes adhesive lamination or extrusion lamination to compostable barrier paper, flexo printing, and zipper insertion on pouching lines. Terminal products are compostable multi-layer pouches for dry foods and non-food personal-care items.
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A compounded polylactic acid (PLA)-based film resin designated INZEA F11 Flexible 40% Bio-Based Film Polylactic Acid is supplied for cast and blown film extrusion where a combination of renewable carbon content and ductile film behavior is required. The grade is formulated to contain 40% bio-based carbon as measured by ASTM D6866-21, with the remainder comprising non-bio-based flexible modifiers and processing aids. The numerical designation F11 identifies a flexible film grade within the INZEA polymer family and separates it from rigid injection-moulding grades and from higher-renewable-carbon film grades that exhibit lower tensile elongation at break. Film converters evaluate INZEA F11 for packaging structures where unmodified PLA fails by brittle fracture during unwind, flexing, or heat-sealing, and where finished-article renewable carbon content must be demonstrated through radiocarbon analysis rather than mass-balance accounting.
Typical values from supplier technical documentation are listed in Table 1. The values are representative for 50 µm cast film unless otherwise stated and are not to be interpreted as release limits; variation across melt lots and film thicknesses is expected.
| Property | Test method | Typical value |
|---|---|---|
| Density | ISO 1183-1:2019 | 1.24–1.26 g/cm³ |
| Bio-based carbon content | ASTM D6866-21 | 40% |
| Melt flow rate at 190°C/2.16 kg | ISO 1133-1:2022 | 6.0–8.0 g/10 min |
| Melting endotherm peak | ISO 11357-3:2018 | 150–160°C |
| Tensile elongation at break, 50 µm film | ISO 527-3:2018 | >300% |
| Tensile stress at break, 50 µm film | ISO 527-3:2018 | 20–30 MPa |
The resin-level bio-based carbon value should not be conflated with finished-film renewable content: printing inks, solventless laminating adhesives, and mineral fillers reduce the measured bio-based carbon of the converted article. Compliance with organic recovery schemes must be demonstrated on the finished article under EN 13432:2000 or ASTM D6400-21, including disintegration after 12 weeks and ecotoxicity testing according to OECD 208. Food-contact status is not automatically conferred by the resin supplier; conversion for direct food contact requires migration testing under FDA 21 CFR 175.300 or Regulation (EU) 10/2011 for the specific food simulant and film thickness.
Industrial compostability and bio-based carbon claims for INZEA F11 are governed by the following boundaries.
| Requirement | Standard | Boundary condition |
|---|---|---|
| Industrial compostability | EN 13432:2000 | Finished film must biodegrade ≥90% in 180 days, disintegrate ≥90% after 12 weeks in industrial composting, and pass ecotoxicity tests under OECD 208. |
| Bio-based carbon | ASTM D6866-21 | 40% of total organic carbon; additives and inks reduce final article value. |
| Food-contact status | FDA 21 CFR 175.300 / Regulation (EU) 10/2011 | Migration testing is required for specific food simulants; resin supplier compliance alone is not sufficient. |
| Moisture content before processing | ISO 15512:2019 or Karl Fischer | ≤0.025%; processing wet resin causes hydrolysis and viscosity loss. |
| Mechanical test preconditioning | ISO 291:2008 | 23°C, 50% RH for ≥40 h before tensile testing. |
Before film extrusion, the resin must be dried to a moisture content below 0.025%. At relative humidity above 60%, exposed granules pick up surface moisture within 30–60 minutes; therefore a closed desiccant-dryer hopper with a dew point below -40°C is the minimum equipment configuration. Drying at 60–80°C for 4–6 hours is the supplier-recommended regime; higher drying temperatures may cause particle fusion in the hopper. The extruder feed throat is kept below 50°C to prevent premature sticking.
In the extruder, the temperature window is constrained by the melting endotherm near 150–160°C and by thermal degradation kinetics above 200°C. PLA chains undergo random scission and lactide reformation at elevated temperature; the zero-shear viscosity declines irreversibly and film gauge variation increases. A single-screw extruder with a moderate compression ratio of 2.5:1 to 3.0:1 and a barrel length of 30 L/D is used on production lines; barrier screws improve melt homogeneity at low screw speeds, but high-shear Maddock mixing sections should be avoided because excessive viscous heating creates local temperatures above the degradation threshold even when barrel set points remain below 195°C.
Barrel set points from feed to die are typically 150–160°C, 165–175°C, 175–185°C, and 180–195°C. Residence time beyond 15 minutes at melt temperature produces gels, yellowing, and a loss of melt strength. Shutdown and material-change procedures use purging compounds compatible with PLA; polyethylene purging is acceptable only if the line is subsequently flushed with a dedicated PLA-compatible purge to avoid interfacial incompatibility during restart. The apparent shear viscosity follows shear-thinning behaviour typical of PLA-based compounds. At 190°C, melt viscosity in the shear-rate range of 100–1000 s⁻¹ is relevant to extrusion dies; at low shear rates below 10 s⁻¹, the higher zero-shear viscosity contributes to die swell. Film processors monitor melt pressure before the screen pack as an indirect quality variable; pressure fluctuations greater than ±1.0 MPa at constant screw speed indicate feed instability, moisture contamination, or viscosity degradation.
When regrind is used, batch-to-batch melt pressure variation becomes measurable at addition levels above 20%; regrind must be dried under the same conditions as virgin resin and screened through a 1.5 mm mesh to remove film flakes that can cause feed-bridging. Edge-trim and slit-scrap regrind is typically reintroduced at 10–15% to maintain stable melt pumping. The material has been used on blown-film lines with die gaps between 0.8 mm and 1.2 mm; wider polyethylene die gaps reduce bubble stability because PLA-based melts exhibit lower elongational melt strength than low-density polyethylene. Bubbles are normally run with a blow-up ratio between 2:1 and 3:1 and frost-line height 200–400 mm above the die; the exact frost line depends on air-ring temperature and gauge. Cast-film lines allow slightly higher melt temperatures but require polished chill rolls at 20–30°C to prevent blocking.
The grade is converted into printed organic waste bags, carrier films, and packaging layers where compostability certification is required on the finished article. Seal initiation occurs at 85–95°C on a hot-bar or impulse sealer; seal strength is highly dependent on film gauge and dwell time. Corona treatment with a surface energy above 38 mN/m is applied for water-based ink and lamination adhesion; however, the treated surface may decay within 7 days in humid storage, requiring re-treatment before printing. The film form has been tested in industrial composting facilities with a thermophilic phase above 58°C; the polymer hydrolyzes and is mineralized by microorganisms. Published data for home composting conditions are limited; the grade is not generally certified for home compostability because lower temperatures and longer time scales do not guarantee full mineralization. A material certified to EN 13432:2000 is not automatically suitable for home compost schemes such as NFT 51-800 or AS 5810.
Conversion of a polyethylene film line to INZEA F11 requires reduced barrel temperatures and narrower die gaps; the same screw that processes linear low-density polyethylene at 200–230°C must be re-profiled for a melt temperature plateau near 185–195°C. The lower melt strength of the PLA-based compound limits maximum line speed in blown-film processes; bubble oscillation and draw resonance are observed when take-up speed exceeds the melt extension rate. In practice, film converters report that single-screw extruders with grooved feed zones maintain higher specific output, but torque limits at low melt temperatures are reached before barrel capacity is fully utilized. On a production line with a 45 mm single-screw extruder with 30 L/D and a 0.8 mm die gap, melt pressure fluctuations above ±1.0 MPa have been associated with feed-bridging of undried regrind in PLA-based compounds; the same failure mode applies to INZEA F11 if regrind moisture is not controlled.
The purge procedure is a critical operational boundary. Residual polyethylene or polypropylene in adapters and dies degrades under PLA processing conditions and can form char, which contaminates subsequent film. A complete line audit for dead spots in screen changers, melt pumps, and die manifolds is required before introduction of INZEA F11. Continuous backflush screen changers with 100–150 µm screens are used because PLA film is sensitive to melt contamination that appears as gel specks. Batch-to-batch melt mass-flow-rate variation in production lots is normally specified as a release window. When switching lots, the melt pressure can shift by 5–10%; operators compensate by adjusting screw speed rather than barrel temperature because the degradation threshold leaves little thermal headroom. This operational constraint is more severe than for polyethylene, where temperature can be increased to manage viscosity.
Differences from polyethylene are most evident in film mechanical properties. INZEA F11 exhibits higher stiffness than low-density polyethylene but lower dart impact at equal gauge; for packaging applications requiring abuse resistance, a thickness increase of 10–20% relative to polyethylene is frequently necessary unless a blending layer is used. The published data for this specific configuration is limited, and no universal thickness equivalency should be assumed. The film also has a service temperature boundary below the glass transition of PLA at 55–60°C; elevated-temperature washing, autoclaving, or hot-fill operations above this range cause dimensional distortion and seal failure.
Compared with unmodified PLA film grades, INZEA F11 shifts tensile failure from brittle fracture to ductile yielding. Unmodified PLA films typically show tensile elongation at break in the range of 2–10% under ISO 527-3:2018, whereas INZEA F11 is formulated to exceed 300%. The formulation trade-off is a lower modulus and a bio-based carbon fraction of 40% rather than the >90% typical for pure PLA. The product therefore competes not with rigid PLA for thermoformed trays but with PBAT-based flexible films that have excellent ductility but lower renewable carbon. Relative to PBAT films, INZEA F11 can raise the renewable carbon content of a compostable laminate while lowering some mechanical performance values such as tear propagation resistance; comparative data should be generated on the specific converting line because film orientation conditions dominate final properties.
Within the INZEA family, F11 differs from injection-moulding formulations by higher melt flow and flexibility. Grades designed for thermoforming may have higher rigidity and a bio-based carbon content above 40%; selection of INZEA F11 is appropriate only where film ductility is the controlling requirement. No single grade can simultaneously maximize renewable carbon and flexibility because the flexible modifiers are non-bio-based in this formulation. Compared with PHA films, INZEA F11 has lower renewable carbon and typically lower raw material cost; quantitative mechanical comparisons are outside public datasheet values. INZEA F11 is not an oxo-degradable additive system and does not fragment under aerobic soil; it is intended for industrial composting where thermophilic temperatures exceed 58°C. Store unopened bags in dry conditions at 15–30°C. Once opened, material should be consumed within 8 hours unless hopper dryers maintain 0.025% moisture. Prolonged storage above 30°C may cause pellet blocking, and exposure to high humidity prior to drying will increase the time required to reach processing moisture specification.