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INZEA FH17 Blown Film Biodegradable Compostable Polylactic Acid

    • Product Name: INZEA FH17 Blown Film Biodegradable Compostable Polylactic Acid
    • Factroy Site: Yudu County, Ganzhou, Jiangxi, China
    • Price Inquiry: admin@ascent-chem.com
    • Manufacturer: Ascent Petrochem Holdings Co., Limited
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    Specifications
    HS Code 820468
    Product Name INZEA FH17
    Material Type Blown Film Biodegradable Compostable Polylactic Acid
    Polymer Base Polylactic Acid (PLA)
    Biodegradability Biodegradable
    Compostability Compostable according to EN 13432, ASTM D6400, OK Compost
    Biobased Content Typically >70%
    Density Approximately 1.25 g/cm³
    Melt Flow Rate Typical 3-6 g/10 min at 190°C/2.16 kg
    Melting Point Approximately 145-155°C
    Glass Transition Temperature Approximately 55-60°C
    Tensile Strength Typical 30-40 MPa
    Elongation At Break Typical >200%
    Tear Resistance Typical 100-200 N/mm
    Optical Haze Typically <5%
    Food Contact Suitable for food contact under EU 10/2011
    Processing Method Blown film extrusion
    Melt Processing Temperature Typical 160-180°C

    As an accredited INZEA FH17 Blown Film Biodegradable Compostable Polylactic Acid factory, we enforce strict quality protocols—every batch undergoes rigorous testing to ensure consistent efficacy and safety standards.

    Packing & Storage
    Packing INZEA FH17 Blown Film Biodegradable Compostable Polylactic Acid is supplied in 25 kg polyethylene-lined paper bags, palletized for transport.
    Container Loading (20′ FCL) 20′ FCL container loading: INZEA FH17 biodegradable compostable polylactic acid blown film resin, palletized, moisture-protected, dry ambient, secured for transport.
    Shipping INZEA FH17 is generally shipped as non-hazardous, moisture-sensitive pellets in sealed foil-lined bags or bulk sacks on pallets. Store in original packaging; keep dry, away from heat, direct sunlight, and contamination. Transport in covered, clean vehicles at moderate temperatures. No special dangerous goods requirements.
    Storage Store INZEA FH17 in a cool, dry, well-ventilated area, away from direct sunlight, heat, moisture, and ignition sources. Keep sealed in original packaging to prevent hydrolysis and contamination. Maintain recommended temperature, typically below 30°C. Avoid oxidizers, strong acids/bases, dust, and static. Use first-in, first-out inventory rotation. Ensure good ventilation and keep containers closed when not in use.
    Shelf Life Typical shelf life is 12 months when stored sealed in original packaging, cool, dry, and protected from direct sunlight.
    Application of INZEA FH17 Blown Film Biodegradable Compostable Polylactic Acid

    What conflicts arise when a 22 µm retail carrier film must retain dart impact after 26 weeks of simulated compost storage?

    Retail carrier conversion with INZEA FH17 blown film biodegradable compostable polylactic acid centers on balancing molecular weight retention during extrusion with post-consumer compostability claims. Compliance for this application is anchored to EN 13432:2000/AC:2005, ISO 17088:2021, and ASTM D6400-21; certification bodies typically require ≥90% biodegradation within 180 days under controlled composting conditions and ≥90% disintegration to a 2 mm sieve fraction within 12 weeks, with ecotoxicity screening per OECD 208. Formulation addition ratio on single-layer lines usually avoids neat material: a blend of 70 wt% INZEA FH17 and 30 wt% PBAT or another certified biodegradable polyester is used to raise dart impact and tear propagation, plus 1.5–2.5 phr of a biodegradable-carrier slip/antiblock masterbatch. Pre-drying is mandatory: 4 h at 80 °C to a moisture content below 250 ppm, with hopper drying air dew point ≤ −40 °C. Extrusion is conducted on a single-screw blown film line with 25–30 L/D barrier screw, 0.8–1.0 mm die gap, melt temperature 170–190 °C, die temperature 185–195 °C, blow-up ratio 2.5–3.0, and frost line height held between 0.8 m and 1.2 m. The bubble is run with chilled air at 8–12 °C because PLA melt strength is lower than LDPE; excessive frost line height produces film blocking and gauge variation exceeding ±8%. Terminal products include t-shirt bags for organic retail chains, lightweight produce carrier bags, and store-level compostable checkout sacks in municipalities that prohibit oxo-degradable additives.

    Municipal source-separated organics programs impose a heavier puncture and leak requirement on compostable caddy liners than on retail bags because contents are often wet and contain hard, irregular food waste. The relevant compliance framework is identical for industrial compostability—EN 13432, ASTM D6400, ISO 17088—but programs in France and Germany frequently add NF T51-800 or DIN EN 13432 conformity, and a few municipalities require a film thickness no greater than 20 µm to reduce compost residue. Formulation addition ratio in this sector commonly uses 85 wt% INZEA FH17 with 15 wt% biodegradable polyester flexibilizer and 2–4 wt% of a compostable black or green masterbatch; filler-bearing masterbatches must not exceed 4 wt% because higher levels lower seal strength and increase pinhole density after gusseting. Production is executed on a high-output blown film line with 30 L/D screw, 1.0 mm die gap, die temperature 180–190 °C, and internal bubble cooling to stabilize a 20–25 µm film at a blow-up ratio of 2.8–3.2. The film is gusseted before wind-up and converted into caddy liners with side-seal or bottom-seal units operating at 60–90 bags/min. A recurring production bottleneck is bubble flutter when line speed exceeds 35 m/min; this is managed by raising top nip pressure and reducing cooling air velocity, but die-lip PLA contamination from earlier PVC or PE runs must be purged with a compostable purge compound to avoid carbonized specks. Terminal products are household food waste caddy liners, countertop collection bags, and residential organic-waste sacks supplied to council programs.

    Soil contact hydrolysis in semi-arid processing tomato mulch systems

    Agricultural mulch film produced from INZEA FH17 must meet a different degradation pathway than industrial compost because the film remains in soil and is not exposed to thermophilic composting conditions. The applicable standard is EN 17033:2018 for biodegradable mulch films, which sets aerobic biodegradation in soil to ≥90% within 24 months at 20–28 °C, acute and chronic ecotoxicity limits, and restriction on substances of very high concern under REACH. Formulation addition ratio for tomato and melon systems often uses 80 wt% INZEA FH17 and 20 wt% PBAT, with 1–2 wt% dispersant aid and, if black mulch is specified, 3–5 wt% of a compostable carbon-black masterbatch based on total film mass. Transparent mulch avoids carbon black but has a shorter deterioration window and lower weed suppression. Downstream production uses a blown film line with 1.2 mm die gap, die temperature 175–185 °C, and blow-up ratio 3.0–3.5 to balance longitudinal and transverse tensile properties; nominal film thickness is 12–25 µm, and thickness across the layflat must be maintained within ±10% because thinner bands fail prematurely along buried edges. The film is perforated online with a pin roller at 20–30 cm intervals for crop respiration, and local soil temperature and moisture at film burial determine the onset of fragmentation—failure is not uniform, and published data for this specific grade in semi-arid Mediterranean soils are limited. Terminal products include black and transparent mulch for processing tomatoes, melons, strawberries, and organic pepper fields, where post-harvest disposal by plowing is intended under EN 17033 certification.

    Indicative blown film processing windows for INZEA FH17 by application
    ApplicationMelt temperature rangeDie gapBlow-up ratioNominal film thickness
    Retail carrier film170–190 °C0.8–1.0 mm2.5–3.022–30 µm
    Caddy liner180–190 °C1.0 mm2.8–3.220–25 µm
    Mulch175–185 °C1.2 mm3.0–3.512–25 µm
    Produce film165–180 °C0.8 mm2.0–2.218–25 µm
    Bakery overwrap170–185 °C0.8 mm2.2–2.820–28 µm
    E-commerce mailer175–190 °C1.0–1.2 mm2.8–3.235–50 µm
    Tea carton overwrap170–180 °C0.8 mm2.0–2.518–22 µm

    At horizontal form-fill-seal lines running 80–110 cycles/min, bakery overwrap films made from INZEA FH17 demand a sealing window broad enough to avoid burn-through yet narrow enough to maintain compostable certification. Compliance for food contact rests on Commission Regulation (EU) No 10/2011 with overall migration ≤10 mg/dm², and in the United States the final blended film must be confirmed under an applicable FDA food-contact notification or exemption because PLA-based films are not automatically covered by 21 CFR 177.1520. Formulation addition ratio is often 70 wt% INZEA FH17 with 30 wt% PBAT to reduce heat-seal initiation temperature, plus 0.5–1.0 phr of a high-clarity anti-block and, where the bakery products have moisture activity above 0.85 aw, 0.5–1.5 phr of a non-migratory antifog masterbatch. Production is run on a blown film line with 0.8 mm die gap, melt temperature 170–185 °C, and blow-up ratio 2.2–2.8; the film is corona-treated at 38–42 dyn/cm on the print side and slit to the required width. The converting step uses heat-seal jaws at 110–130 °C, pressure 1.5–2.0 N/mm², and dwell 0.2–0.4 s, with seal strength tested after 24 h at 23 °C and 50% RH; lap seals are preferred over fin seals because localized thinning at fold edges creates seal integrity failure. Terminal product types include bread bags, croissant pouches, dry bakery wraps, and cookie sleeves where industrial compostability is specified by the bakery brand.

    When e-commerce mailer converting demands low-temperature puncture retention after gusset folding

    E-commerce mailer applications expose INZEA FH17 to cold-chain parcel handling and repeated flexing at fold lines, which makes puncture resistance after folding the primary process design criterion. This non-food application is governed by EN 13432 or ASTM D6400 for compostability, REACH Regulation (EC) No 1907/2006 for additives and inks, and CONEG TPCH or EU Packaging Directive 94/62/EC for heavy-metal packaging limits. Formulation addition ratio is typically 80 wt% INZEA FH17 and 20 wt% polybutylene adipate terephthalate, with 1.0–1.5 phr anti-block and 2–4 wt% of an opaque compostable masterbatch to reduce product see-through. Extrusion is performed with a 1.0–1.2 mm die gap, melt temperature 175–190 °C, and blow-up ratio 2.8–3.2, yielding a nominal film thickness of 35–50 µm; post-bubble gusseting is applied to create a flat web with two side folds. The converting line runs at 40–70 bags/min with bottom-seal impulse sealing and kiss-cut adhesive strip application; the adhesive must be compostable or removable because solvent-borne acrylic adhesive residue will fail the disintegration portion of EN 13432. A known production mode is closure at 4 °C, where seal impact strength decreases relative to 23 °C; condition incoming film for 24 h at 20–25 °C before cutting to avoid curl. Terminal products are compostable poly mailers for garments, footwear dust bags, and small non-food e-commerce shipments where brand owners require an end-of-life compostability claim.

    Blown film die lip deposition and slip masterbatch response in tea carton overwrap

    Transparent overwrap for dry grocery cartons uses the high-clarity capability of INZEA FH17 but introduces a die-lip deposition problem that is not observed with LDPE because PLA and its additive package can form low-molecular-weight residues at extended run lengths. Compliance for carton overwrap includes REACH Regulation (EC) No 1907/2006, heavy-metal limits in 94/62/EC, and, where the overwrap contacts printed food carton interiors indirectly, migration verification under EU No 10/2011 may be required by the converter even though the film is not a direct food-contact layer. Formulation addition ratio is 100 wt% INZEA FH17 with 1.0–1.5 wt% of a synthetic silica anti-block and 0.3–0.8 wt% of an ester-based slip additive; levels above 0.8 wt% reduce clarity and raise haze beyond 3%, which is rejectable for high-volume tea carton display. Extrusion is conducted at a melt temperature of 170–180 °C, die gap 0.8 mm, and blow-up ratio 2.0–2.5; the bubble is quenched with 10–15 °C air and the layflat is corona-treated at 42 dyn/cm. Run lengths above 8 h may produce surface deposits near the die lip; periodic purge with a PLA-compatible purge compound every 6–8 h is used to maintain clarity and reduce gels. Terminal product types are tea carton overwrap, cosmetic carton film, and clear display wraps for boxed dry grocery products that require industrial compostability.

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    Certification & Compliance
    More Introduction
    INZEA FH17 is a biodegradable and compostable polylactic acid compound formulated specifically for blown film extrusion of flexible packaging, organic-waste collection liners, and agricultural mulch films. The grade is supplied as cylindrical pellets with a bulk density in the range 0.78–0.85 g/cm³; solid-state density is typically 1.24–1.26 g/cm³ when conditioned at 23 °C and 50% RH and determined according to ISO 1183-1:2019. Melt-volume rate, used as a lot-release index rather than a direct processing parameter, is commonly reported between 4 cm³/10 min and 8 cm³/10 min at 190 °C under 2.16 kg load per ISO 1133-1:2022. Intended film thickness spans 15–80 µm; outside this interval bubble stability, tear performance, and heat-seal consistency require production-scale verification. The material is neither a PBAT-rich elastomer nor an unmodified PLA homopolymer. It is a PLA-dominant blown film compound containing biodegradable melt-strength and impact-modifying constituents selected to maintain industrial compostability while reducing the brittleness and bubble instability observed with neat polylactic acid.

    What Limits the Melt Processing Window on LDPE-Type Blown Film Equipment?

    The primary processing boundary is hydrolytic degradation. Pellets exposed to ambient humidity should be desiccant-dried at 65–80 °C for 4–6 h until residual moisture is below 250 ppm; higher moisture levels reduce melt viscosity, generate pinholes, and produce surging or gel-like defects at the die. Drying should be performed with a desiccant-bed dew point of −30 °C or lower, and dried pellets should be conveyed with dry air rather than ambient plant air. On a 45–65 mm single-screw extruder with 24:1–30:1 L/D and a conventional three-zone polyethylene screw, barrel settings commonly begin at 150–165 °C in the feed zone, rise to 170–185 °C in the metering zone, and hold the die at 165–180 °C. Screw speed on a 50 mm machine typically falls between 40 min⁻¹ and 80 min⁻¹. Melt temperature should remain below 200 °C to prevent lactide evolution, depolymerization, and film discoloration. Blow-up ratio is normally maintained between 2.0 and 2.8, with frost-line height set at 2–3 die diameters. Higher blow-up ratio improves transverse-direction tear but destabilizes the bubble because the compound has lower extensional viscosity than LDPE. Die gaps of 0.8–1.2 mm are recommended for monolayer film. On a production line equipped with a 55 mm extruder, 25:1 L/D screw, and 250 mm spiral-mandrel die, melt-pressure fluctuation should remain within ±1.0 MPa to maintain a stable frost line and gauge variation below ±2 µm. Unlike LDPE, feed-zone overshoot above 190 °C can cause pellet softening and feed-throat bridging if hopper cooling is not active. Coextrusion with other INZEA grades or plasticized PLA layers is possible only after matching shear-viscosity curves between 100 s⁻¹ and 1000 s⁻¹ to avoid interfacial instability. Post-industrial regrind from edge trim and start-up scrap can be reintroduced at 10–20 wt% if the fluff is densified and dried below 300 ppm moisture. Undried regrind generates acetic-acid odor at the die and measurably reduces melt strength. The compound is incompatible with polyolefin melt streams: as little as 2 wt% polyethylene or polypropylene contamination reduces weld-line strength and creates delamination defects. Dedicated hoppers, vacuum loaders, and purging with acrylic-based compounds are required when changing from LDPE or PP. Film produced from INZEA FH17 should be stored below 40 °C and 60% RH to prevent blocking and hydrolytic aging before conversion.

    Compostability and Disintegration Performance Under EN 13432 and ASTM D6400

    Compostability claims must be evaluated on the final film article, because gauge, printing inks, adhesives, and processing additives influence biodegradation rate and disintegration behavior. The resin is formulated to support the four-stage compostability requirements of EN 13432:2000: characterization, aerobic biodegradation, disintegration, and ecotoxicity. Aerobic biodegradation is measured under controlled composting conditions according to ISO 14855-1:2012; compliance requires 90% mineralization relative to the reference material within 180 days. Disintegration under ISO 16929:2021 requires that after 12 weeks no more than 10% of the original dry mass remains on a 2 mm sieve. Ecotoxicity is evaluated by plant germination and earthworm acute toxicity tests, typically following EN 13432:2000 Annex E and OECD 208. For North American markets, ASTM D6400-23 applies. Biodegradation under that scheme is measured by ASTM D5338-15, and the material must meet the same 90% mineralization threshold within 180 days. Disintegration, heavy-metal limits, and ecotoxicity follow the corresponding ASTM protocol. Certification marks should be verified against the lot-specific certificate because compound certification alone does not automatically extend to printed, laminated, or adhesive-bonded films. Heavy-metal limits are controlled through the compounding formulation, which avoids intentionally added persistent fluorinated processing aids and heavy-metal catalysts.
    CriterionTest methodAcceptance threshold
    Aerobic biodegradationISO 14855-1:2012 / ASTM D5338-15≥90% mineralization in 180 days
    DisintegrationISO 16929:2021 / ASTM D6400-23≤10% dry mass retained on 2 mm sieve after 12 weeks
    EcotoxicityOECD 208; EN 13432:2000 Annex ENo germination delay or acute earthworm toxicity
    Heavy metalsEN 13432:2000 Annex A; ASTM D6400-23Below regulatory limits for compost quality

    When INZEA FH17 Replaces LDPE in Compostable Packaging Lines

    Direct drop-in replacement for LDPE is not possible. The compound has a narrower melt-processing window and lower melt strength, so maximum take-off speed is typically reduced by 20–40% relative to LDPE at equivalent gauge. Bubble cooling must be rebalanced by reducing blow-up ratio or increasing frost-line height. In direct film comparisons at 25 µm thickness, PLA-based blown film grades of the FH17 class show tensile modulus in the machine direction between 800 MPa and 1200 MPa when tested by ISO 527-3:2018. Unmodified PLA blown films generally exceed 2500 MPa, while PBAT-rich blown films are commonly below 500 MPa. This places INZEA FH17 between stiff PLA homopolymer and low-modulus PBAT copolyester. Elongation at break in machine direction for INZEA FH17 is typically in the range 150–250% by ISO 527-3:2018, compared with 5–20% for unmodified PLA blown film and 400–700% for PBAT-rich compounds. That elongation window is sufficient for bag manufacture and twist-closure applications but is not equivalent to PBAT-dominated stretch films. Tear resistance measured by ISO 6383-2 is intermediate; published data for this specific configuration is limited, and converter trials are required because tear values depend strongly on draw ratio, frost-line height, and die-gap selection. The presence of PLA raises the heat-seal initiation temperature to approximately 95–110 °C, which is above PBAT-rich seal layers and may require jaw-temperature setpoint adjustment on high-speed bag machines. Peel-seal windows should be established on the final film because corona treatment and antistatic coatings shift seal initiation. Relative to unmodified PLA blown film, INZEA FH17 reduces bubble flapping and excessive neck-in through improved low-frequency strain hardening, but it does not reach the extensional melt strength of LDPE. Relative to PBAT-rich blends, the grade provides higher stiffness and higher renewable carbon content because PLA is the dominant phase. Renewable carbon content can be quantified by ASTM D6866-22 when a bio-based carbon claim is required. However, the material is not recommended for long-term liquid packaging or thermal sterilization above 50 °C, because PLA-rich films soften near the glass transition and lose seal strength. Moisture-vapor transmission is higher than LDPE and lower than starch-based blown film compounds, which affects produce-packaging shelf-life and condensation behavior.
    Property at 25 µm film thicknessINZEA FH17 classUnmodified PLA blown filmPBAT-rich blown film
    Tensile modulus, MD800–1200 MPa2500–3500 MPa300–500 MPa
    Elongation at break, MD150–250%5–20%400–700%
    Melt strength and bubble stabilityIntermediateLowHigh
    Heat-seal initiation95–110 °CNarrow, often above 110 °C70–90 °C
    Renewable carbon contentHigher than PBAT-rich filmsHighLower
    Applications include certified compostable shopping bags, produce bags, magazine overwrap, and organic-waste liners where the final article enters industrial composting or anaerobic digestion feedstock. The compound is not intended for marine biodegradation claims or home-compost certification unless separately validated. For food-contact use, migration testing under EU Regulation 10/2011 or the applicable FDA conditions of use must be performed on the final printed, sealed, and coated article; resin certification alone does not confer food-contact approval. If curbside compost acceptance is required, the finished film must meet the specification of the local certification program, for example EN 13432:2000 or ASTM D6400-23, and carry the corresponding conformity mark.
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