| HS Code | 483268 |
| Product | INZEA F16 Blown Film High Starch High Modulus Polylactic Acid |
| Chemical Family | Polylactic acid (PLA) with high starch content |
| Form | Pellets |
| Density | 1.35 g/cm³ |
| Melt Flow Rate | 3.0 g/10 min (190°C/2.16 kg) |
| Melting Temperature | 150 °C |
| Glass Transition Temperature | 55 °C |
| Tensile Modulus | 3000 MPa |
| Tensile Strength | 40 MPa |
| Elongation At Break | 5% |
| Flexural Modulus | 3500 MPa |
| Charpy Impact Strength | 15 kJ/m² |
| Haze | 30% |
| Gloss | 85 (45°) |
| Water Vapor Transmission Rate | 120 g/m²/day |
| Oxygen Transmission Rate | 700 cm³/m²/day |
| Renewable Content | >80% |
| Compostability | EN 13432 certified |
| Processing Temperature | 160–180 °C |
| Starch Content | High |
As an accredited INZEA F16 Blown Film High Starch High Modulus Polylactic Acid factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.
| Packing | INZEA F16 Blown Film High Starch High Modulus Polylactic Acid is packaged in 25 kg sealed moisture-resistant bags on pallets. |
| Container Loading (20′ FCL) | Container loading (20′ FCL): INZEA F16 Blown Film High Starch High Modulus Polylactic Acid, palletized and secured for safe ocean transit. |
| Shipping | INZEA F16 is shipped as non-hazardous, moisture-sensitive resin pellets in sealed foil-lined bags, 25 kg sacks, or octabins on pallets. Transport in dry, ventilated vehicles at moderate temperatures, avoiding heat, sunlight, and humidity. Not classified as dangerous goods; standard freight applies. Keep sealed until use. |
| Storage | Store INZEA F16 in a cool, dry, well-ventilated area, away from direct sunlight and heat. Keep sealed in original packaging to prevent moisture absorption, which can degrade the starch/PLA blend. Recommended conditions: below 30°C and low relative humidity. Avoid strong oxidizers and incompatible materials. Reseal opened bags promptly. Use first-in, first-out stock rotation. Protect from moisture and contamination. |
| Shelf Life | INZEA F16 has a shelf life of approximately 12 months when stored cool, dry, and sealed in original packaging. |
For INZEA F16 blown film high starch high modulus polylactic acid, single-station blown-film lines built around a 50 mm barrier screw with L/D 28:1 reach a stable bubble window only after desiccant drying reduces pellet moisture to ≤0.10 % and the melt temperature is maintained in the 150–170 °C range. The carrier-bag segment typically starts at 80–100 wt% INZEA F16 with 0–20 wt% PBAT co-polyester and 0.5–2.0 wt% anti-block masterbatch, because the high modulus suppresses dart-impact energy absorption unless the co-polyester modifier is incorporated. On the extrusion line, a die gap of 1.0–1.2 mm and a blow-up ratio of 2.2:1–3.0:1 are used with a low-pressure dual-lip air ring; incoming resin lot flow properties are checked under ISO 1133-1:2022 at 190 °C with 2.16 kg load, and the die-head temperature is held below 170 °C to control starch decomposition and gel speck generation. The resulting web, normally 15–35 µm, is converted into T-shirt bags, loop-handle bags, and die-cut handle bags. Finished-product conformity is evaluated under EN 13432:2000, ASTM D6400-21, and ISO 17088:2021; dart impact is tested by ASTM D1709 and tear propagation by ASTM D1922.
Converting INZEA F16 into organic waste collection liners forces a trade-off between compostability certification and wet-load mechanical integrity. The film is typically formulated with 85–100 wt% INZEA F16 and 0–15 wt% PBAT; functional additive loading is kept below 1.5 wt% because excessive slip concentrate reduces film friction below the level required for automatic bag dispensing in municipal collection caddies. The blown-film line should use a 1.2 mm die gap, a 2.5:1–3.0:1 blow-up ratio, and a frost-line position 3–5 die diameters above the die to compensate for the reduction in melt strength caused by the starch phase. Barrel set-points are limited to 140–165 °C; operation above that range accelerates viscosity drift and gel formation. Pellets stored at ambient relative humidity above 60 % require desiccant drying before extrusion, and regrind use is constrained by the heat-history sensitivity of the starch phase. Terminal products are kitchen caddy liners, municipal kerbside organics bags, and yard-waste sacks in regions requiring compostable bag programs. Certification for this segment must satisfy EN 13432:2000 for composting and EN 13592:2017 for household waste sack performance, while North American shipments are assessed under ASTM D6400-21; film tensile properties are tested using ISO 527-3 and tear resistance using ISO 6383-2.
When a mulch film is specified to be ploughed into the soil after harvest, the relevant certification pathway shifts from compostability to soil biodegradability under EN 17033:2018. Published agricultural trial data for INZEA F16 in this exact film grade is limited; however, blown-film converters have evaluated starting formulations at 75–100 wt% INZEA F16 with 0–25 wt% PBAT and 0–2 wt% carbon-black masterbatch where UV screening is required. The film is processed on blown-film lines with a 1.0–1.2 mm die gap and a 2.5:1–3.0:1 blow-up ratio, producing 10–20 µm webs that must withstand mechanical laying on tractor-mounted mulch layers without splitting along the drum folds. Terminal product types are black, white, and clear biodegradable mulch films for vegetable and specialty-crop production. Soil biodegradation testing is conducted according to ISO 17556:2019, and field-trial protocols follow EN 17033:2018; because published data for the interaction of the high-starch matrix with multi-season soil burial is limited, commercial field validation remains mandatory.
In bakery and produce packaging, the high modulus of INZEA F16 creates sufficient film stiffness for low-gauge down-gauging, but the heat-seal window narrows because starch-rich PLA recrystallizes at the seal jaw and can produce brittle seams if dwell time is excessive. The recommended starting formulation is 100 wt% INZEA F16 with 1–3 wt% anti-block masterbatch and 0.5–1.5 wt% slip masterbatch; PBAT is omitted where high-stiffness film handling is required, but may be added at 5–15 wt% to improve tear resistance. Extrusion is performed through a 0.8–1.0 mm die gap at a blow-up ratio of 2.0:1–2.5:1, and the web is corona-treated to 38–42 mN/m for flexographic or digital ink adhesion. Finished film thicknesses of 10–25 µm are converted into bread bags, produce bags, and dry food pouches. Food-contact status must be confirmed under Regulation (EU) No 10/2011 with an overall migration limit of 10 mg/dm² and under FDA 21 CFR 177.1500 for polyester copolymer components; overall migration testing follows EN 1186-1. The material is not appropriate for long-term direct contact with high-moisture acidic foods because starch swelling can occur at the film surface.
A flat-die extrusion-coating line running a 65 mm extruder applies a 100 % INZEA F16 melt web at 15–25 g/m² onto paper or board to form compostable lamination for dry bakery and confectionery packaging; the coated structure is assessed for compostability under EN 13432:2000, while food-contact status of the paperboard side falls under BfR Recommendation XXXVI or FDA 21 CFR 176.170, and the resulting finished products are compostable paper cups, folding-carton windows, and tray liners.
Mailer conversion failures observed on commercial impulse-sealing equipment are most commonly traced to film gauge variation rather than the base resin alone; therefore the blown-film die gap is set at 1.2 mm and the blow-up ratio at 2.8:1–3.2:1 to distribute thickness within ±5 % before the bubble is collapsed. The starting formulation for mailer film is 70–90 wt% INZEA F16 with 10–30 wt% PBAT co-polyester and 0.5–2.0 wt% anti-block masterbatch; this blend is required because the high modulus of the base resin reduces cold-temperature dart-impact energy absorption. Film thickness is typically 30–50 µm, and the web is converted through automatic cutting, folding, and impulse sealing into poly mailers, shipping envelopes, and document mailers. Compliance for these finished goods is evaluated under EN 13432:2000 and ASTM D6400-21, seal strength is tested according to ASTM F88/F88M, dart impact according to ASTM D1709, and substance communication is handled under REACH (EC) No 1907/2006. The material is not recommended for mailer applications exposed to prolonged outdoor weathering because the starch phase can absorb humidity and alter seal consistency.
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INZEA F16 Blown Film High Starch High Modulus Polylactic Acid is a pelletized thermoplastic compound formulated for blown-film extrusion. The material combines a polylactic acid continuous phase with a high renewable starch fraction; the starch contributes renewable carbon and modulus, while the PLA phase provides melt processability and industrial compostability behavior. The F16 model designation identifies a film-grade rheology package rather than a general-purpose PLA injection-moulding material. Primary applications include compostable carrier bags, organic waste bags, retail packaging films, and agricultural mulch films intended for industrial composting. The product is not a drop-in replacement for polyethylene on high-speed lines; pre-drying, melt-temperature control, and die-lip maintenance are mandatory. Published data for this specific configuration is limited, but the grade is reported to require a narrower processing window than polyolefin blown-film resins.
Specifications used for preliminary equipment sizing are typically reported as follows: density 1.25–1.28 g/cm³ under ISO 1183-1; melt flow index 2–4 g/10 min at 190 °C and 2.16 kg under ISO 1133-1:2022; blown-film tensile modulus 3000–3800 MPa under ISO 527-3; elongation at break 4–10% under ISO 527-3. Residual moisture after drying should be below 0.025 wt% by ISO 15512 or Karl Fischer titration. These values place the F16 material in the high-modulus, low-elongation quadrant; the modulus enables thin-gauge film production, but the low ductility requires careful control of edge tears and dart impact.
The high starch loading modifies the solid-state mechanical response beyond the values visible in a standard tensile curve. In high-starch PLA films, the starch-rich domains restrict cold drawing, maintaining tensile modulus above 2500 MPa at 23 °C while elongation at break remains below 10%. Unlike plasticized PLA, the starch does not act as an internal lubricant; it raises moisture uptake and increases sensitivity to humidity-induced dimensional change. Conditioning before mechanical testing should follow the standard atmosphere of 23±2 °C and 50±5% RH for at least 40 h; test results obtained without conditioning can overstate stiffness and understate strain at break.
| Material class | Tensile modulus | Elongation at break | Moisture uptake | Bubble stability |
|---|---|---|---|---|
| INZEA F16 high-starch PLA | 3000–3800 MPa | 4–10% | Moderate-high | Narrow; stable only after pre-drying |
| Unmodified PLA blown-film grade | 3000–3500 MPa | 2–6% | Low-moderate | Narrow; brittle if quenched too rapidly |
| PBAT/starch blown-film compound | 80–200 MPa | 400–800% | Moderate | Broad; high melt flexibility |
The comparison highlights the central performance conflict: high starch in PLA raises stiffness and renewable content but reduces plastic deformation capacity and increases humidity sensitivity. PBAT-rich compounds offer puncture absorption through yielding; F16 resists deformation until fracture. This distinction determines application suitability: F16 is selected for down-gauged bags requiring stiffness, not for stretch wrap, elastic bands, or heavy-duty garbage bags.
High-starch PLA has a narrower processing window than LDPE because starch degrades above 180 °C and PLA hydrolyzes in the presence of residual moisture. Drying is required in a desiccant drier at 70±5 °C for 4 h, with air dew point at or below -40 °C. Pellets should not be dried above 80 °C; higher temperatures cause pellet surface tack and can agglomerate starch at the feed throat. The target moisture after drying is below 0.025 wt%. If residual moisture exceeds 0.05 wt%, hydrolytic chain scission occurs at melt temperatures above 165 °C, producing a measurable loss of bubble tension and lower intrinsic viscosity.
On a single-screw blown-film line with a 25:1–30:1 L/D barrier screw, the barrel profile should be ramped from 145 °C in the feed zone to 170±5 °C in the metering zone. Die and adapter temperatures are typically held at 170–175 °C; the practical melt-temperature window is approximately ±5 °C around the die set point. A die gap of 1.0–1.5 mm and blow-up ratio of 2.0–3.0 are appropriate starting values. Frost-line height is usually higher than for LDPE to allow the PLA crystalline domains to develop before collapse; early freezing produces blocking, crease cracks, and film stickiness at the nip.
Melt residence time in the die should be minimized. If die pressure exceeds 250 bar, the die gap should be opened before the screw speed is reduced, because residence-time reduction lowers starch browning at the die lip. Screw speed on a 45 mm extruder is typically limited to 40–80 rpm for stable melt output; higher speeds generate shear heating that can overshoot the melt-temperature ceiling even when barrel set points remain unchanged.
The melt-phase behavior of high-starch PLA differs from polyolefins in two ways. First, the addition of starch increases shear thinning, so die pressure often falls as screw speed increases; this can mislead operators into raising screw speed to improve output. Second, high starch loading reduces extensional strain hardening relative to LLDPE, so bubble stability depends more on thermal setting than on polyolefin-like melt strength. The practical consequence is that blow-up ratio and frost-line height must be controlled together: a low stalk height with a high blow-up ratio can overstretch the melt and generate thickness variation, while an overly high frost line can produce secondary crystallization and blocking at the nip.
Production-scale experience with high-starch PLA blown-film grades shows that die lip starch deposition accumulates after continuous running and appears as amber specks or edge deposits. The condition is not corrected by lowering the die temperature alone, because the deposited material is partly cross-linked starch and degraded PLA. Periodic purging with a commercial PLA purge compound or LDPE before shutdown is used to remove die lip build-up; mechanical cleaning with brass tools is required if the deposit hardens. Bubble vertical oscillation in the stalk region is frequently observed when melt temperature exceeds 175 °C or when residual moisture remains above 0.05 wt%. Increasing screw speed under these conditions usually worsens the oscillation because shear heating moves the melt further outside the permissible window.
Additive selection is constrained by the PLA ester chemistry. Amine-containing processing aids should be avoided because they accelerate transesterification and chain scission at melt temperatures above 170 °C. Acidic additives that drive moisture into the starch phase can reduce melt strength. Water-borne filler masterbatches must be dried with the base resin to avoid localized hydrolysis.
Compostability claims for F16 are valid only for the final packaging article. Certification under EN 13432:2000 requires chemical characterization, biodegradation of at least 90% within 6 months, disintegration of at least 90% after 12 weeks, and conclusive ecotoxicity testing. Under ASTM D6400-23, the corresponding threshold is 90% biodegradation within 180 days and 90% disintegration within 12 weeks. The high starch fraction accelerates microbial assimilation relative to neat PLA, but pigments, printing inks, and adhesive laminates can retard disintegration. Grade certification does not automatically extend to printed or laminated final structures.
Food-contact status must be verified separately. Biobased and compostable designations do not confer automatic compliance with FDA 21 CFR 177.1520 or Regulation (EU) No 10/2011. Starch, compatibilizer, slip agent, and pigment migration limits are evaluated in the final packaging configuration.
In converting operations, film from F16 may require corona treatment to raise surface energy to at least 38 mN/m for water-based ink adhesion. The treated surface decays faster under high humidity than neat PLA because surface starch domains reorient. Slitting edges should be inspected for micro-cracks before bag making; high-modulus low-elongation films propagate edge defects under sudden tensile loads. Bags produced from F16 are generally run at 18–35 µm thickness; down-gauging below 15 µm is not recommended without impact modification because dart impact and tear resistance fall below typical distribution-cycle requirements.
Water-vapour transmission rates of high-starch PLA films are higher than those of polyolefin films when measured under ASTM E96/E96M desiccant method. The starch phase increases hydrophilicity, so films stored in high-humidity environments lose modulus and become more dimensionally sensitive. This limits applications in frozen-food packaging where condensation and ice contact are frequent unless a barrier coating or lamination is used. Published data for the F16 grade under specific barrier coatings is limited, and end-product testing is required.
Compared with unmodified PLA blown-film grades, F16 reduces dependence on synthetic impact modifiers and increases renewable-carbon content but raises equilibrium moisture uptake and lowers clarity. Compared with PBAT/starch compounds, F16 has higher tensile modulus and lower puncture-absorption capacity. The final selection depends on whether the application requires stiffness and thin-gauge economics or softness and high elongation. For industrial and retail waste bags, F16 is usually considered where compostability and stiffness are more important than elastic recovery.
End-of-life behavior depends on the receiving infrastructure. The product is intended for industrial composting, not home composting or marine biodegradation. In anaerobic landfill conditions, PLA degrades slowly, and the high starch fraction may increase biogas potential but does not confer home compostability. Waste collectors should route F16 films to industrial composting facilities operating at 58±2 °C, moisture above 50%, and active aeration; these conditions correspond to the EN 13432:2000 test environment.
Storage conditions influence downstream process stability. Sealed bags should be kept at temperatures below 30 °C and relative humidity below 50%. Once opened, the product should be processed within 24 h; if not, re-drying is required before blown-film extrusion. Damaged bags exposed to ambient humidity for more than one shift should not be processed without moisture analysis, because the starch phase preferentially absorbs water and can create film defects that are not visible until after bubble collapse.