Standard Disintegration Yield Metrics in Aqueous Dispersion Barrier Substrates
Aqueous dispersion barrier board yields 85 to 94 percent usable fiber depending on coat weight, pulping temperature, and slotted screen aperture dimensions.

Vat
Hydrapulper rotor design and slurry consistency govern the initial disintegration rate of aqueous dispersion barrier papers. Polymer coatings formulated from styrene-butadiene, polyacrylates, or vegetable-oil-derived resins form hydrophobic surface films on cellulosic fibers. Unlike traditional polyethylene extrusion coatings that remain as continuous sheets during hydrapulping, aqueous dispersion polymers break into discrete fragments under high-shear agitation.
The physical breakdown velocity dictates how rapidly pulp slurries achieve complete fiber defibering during stock preparation.

Hydrapulper Shear and Mechanical Breakdown
Mechanical energy input breaks the paper matrix into individual cellulosic fibers during industrial slushing operations. Industrial pulping operates across three primary consistency regimes. Low consistency hydrapulping operates between 3 percent and 6 percent solids, applying rapid rotor speeds to generate hydrodynamic shear.
High consistency pulping operates between 12 percent and 18 percent solids, relying on fiber-to-fiber friction to strip surface coatings from base sheets. High consistency pulping reduces the mechanical energy required per metric ton of dry fiber while minimizing fiber shortening.
Rotor geometry modulates energy transfer efficiency. Helical rotors generate axial flow patterns that promote uniform fiber agitation, preventing unpulped board flakes from settling in stagnant zones. Pulper residence time varies between 10 minutes and 25 minutes depending on water temperature and chemistry.
Operating water temperatures between 40 degrees Celsius and 50 degrees Celsius soften synthetic polymer matrices, accelerating fiber detachment without melting thermoplastic components into tacky masses.
Hydrapulping aqueous dispersion barrier substrates at neutral pH yields coarse polymer fragments that deposit on machine wires during papermaking.

Polymer Binder Chemistry and Hydrolysis Dynamics
Aqueous barrier coatings rely on synthetic polymers such as styrene-butadiene rubber, polyacrylates, or bio-based wax emulsions. Acrylic-based dispersions contain carboxyl groups that ionize under alkaline conditions. Adjusting pulper pH to 8.5 or 9.0 using sodium hydroxide accelerates polymer hydration, causing binder films to swell and detach from wood fibers.
Unmodified styrene-butadiene coatings exhibit minimal chemical swelling, depending entirely on mechanical shear for physical disintegration.
Crosslinking density within the dispersion film dictates mechanical resistance. Highly crosslinked polymers designed for heat-seal performance or water vapor barrier resistance resist mechanical cleavage during pulping. These crosslinked structures fracture into stiff, coarse flakes rather than dispersing into microscopic particles.
Slurry chemistry, temperature, and pulper residence time interact directly to fix the yield of usable pulp.
| Coating Chemistry | Pulper Consistency (%) | Slurry pH Range | Pulper Temp (°C) | Disintegration Time (min) | Visual Flake Fraction (%) |
|---|---|---|---|---|---|
| Styrene-Acrylic Dispersion | 15.0 | 8.5 – 9.0 | 45 | 12 | 1.8 |
| Unmodified Polyacrylate | 12.0 | 8.0 – 8.5 | 40 | 15 | 2.4 |
| Crosslinked Acrylic Copolymer | 15.0 | 7.0 – 7.5 | 25 | 25 | 8.6 |
| Styrene-Butadiene Latex | 5.0 | 7.0 – 7.5 | 40 | 20 | 6.2 |
| Bio-based Wax/Shellac Dispersion | 12.0 | 9.0 – 9.5 | 50 | 10 | 0.9 |
| Testing conducted per ISO 5263 at 3,000 rotor revolutions, conditioned at 23 °C and 50% RH prior to repulping mass balance evaluation. | |||||
Material suppliers frequently state that unpulped polymer flakes result entirely from insufficient pulping residence time or low water temperature rather than resin crosslinking density.

Sieve
Laboratory fractionating devices measure the physical separation of cellulosic pulp from non-disintegrable polymer film fragments. Standardized recyclability evaluation frameworks rely on slotted vibrating screens to isolate unusable rejects from clean fiber slurries. The quantity and physical dimensions of material retained on these screen plates define the disintegration yield metric for packaging substrates.

Which Screening Mesh Size Dictates Particle Accept Rates?
Slotted laboratory screens operating with 0.15 millimeter aperture widths filter coarse dispersion flakes from the pulp stream. Standard protocols, including PTS-RH 021/97 and the CEPI Recyclability Laboratory Test Method Version 2, designate the 0.15 millimeter slotted Somerville fractionator as the primary bench instrument. Accept yields drop rapidly when polymer film fragments exceed slot width dimensions.
Screen slots retain coarse barrier particles while allowing individualized wood fibers to pass into the filtrate stream.
Fiber recovery calculations compare the oven-dry mass of accepted fibers against the total starting dry mass of the packaging sample. High-yielding barrier substrates achieve accept values above 90 percent after primary fractionation. Substrates generating rigid, non-disintegrating barrier flakes blind screen apertures, reducing total flow rates and inflating recorded reject figures.

Somerville Fractionation and Accept Yield Evaluation
Standardized testing protocols mandate specific agitation parameters to isolate reject fractions from recovered cellulosic stock. The 92 percent accept yield metric rests on PTS-RH 021/97 Category A standard testing at 40 degrees Celsius for 10 minutes at 6 percent consistency. Lowering water temperature to 20 degrees Celsius drops this yield figure to 81 percent.
Agitation forces inside the Somerville screen wash residual loose fibers off larger polymer fragments, preventing usable wood pulp from being misclassified as reject waste.
Testing at 45 degrees Celsius with a 0.15 millimeter slotted Somerville screen establishes the baseline standard accept yield threshold of 92 percent for repulped stock.
Quantifying reject composition requires separating organic cellulosic material from synthetic polymer mass. Rejects washed from the screen plate undergo drying at 105 degrees Celsius until mass constancy is reached. Subsequent calcination inside a muffle furnace at 525 degrees Celsius determines the inorganic filler content present in the reject residue.
Fiber loss occurs when unseparated cellulose remains bound to polymer fragments.
- Incomplete coating disintegration produces oversized polymer flakes that clog screen slots during fractionation.
- Fibre agglomeration binds usable cellulosic material to insoluble resin particles, artificially increasing reject mass.
- Screen blinding occurs when tacky dispersion residues accumulate over slotted apertures, halting filtrate flow.
Clause 4.2 of the CEPI recyclability test protocol mandates a maximum total reject limit of 15 percent, shifting financial responsibility for process waste directly to the board converter when unseparated dispersion particles exceed the threshold.

Fouling
Sub-millimeter polymer particles passing through fractionating screens enter the white water circuit of the paper machine. Dispersion coatings that disintegrate into particles smaller than 0.15 millimeters avoid capture on Somerville reject screens. These fine polymer particles behave as micro-stickies within industrial stock preparation systems, presenting operational risks during sheet formation.

Particle Size Distribution and Agglomeration Mechanics
Dispersion polymers fragment into distinct dimensional populations under mechanical agitation in the repulper. Macro-stickies measure greater than 100 micrometers in diameter, while micro-stickies range between 1 micrometer and 100 micrometers. Micro-dispersed particles below 1 micrometer remain suspended in process water without immediate deposition.
Shear forces dictating particle disintegration determine which size fraction dominates the repulped slurry.
Industry laboratory consensus cites 50 micrometers as the absolute threshold between benign micro-stickies and damaging macro-stickies, yet experimental data across different repulping circuits remains inconclusive. A prudent buyer enforces a conservative 30 micrometer filtration benchmark in supply contracts to mitigate runnability risks. Changes in system pH, ionic strength, or temperature cause micro-stickies to agglomerate into larger tacky complexes within stock chests.
- Sample repulped stock slurry from the pulper outlet at 4 percent consistency.
- Dilute slurry with distilled water to 0.5 percent consistency in a temperature-controlled beaker.
- Pass the diluted suspension through a 0.15 millimeter slotted fractionating plate for 20 minutes.
- Collect collected screen rejects on pre-weighed filter paper and dry at 105 degrees Celsius.

Screen Blinding and Deposition Risks
Tacky polymer particles coalesce on forming fabrics, press felts, and drying cylinders during sheet consolidation. Thermal energy in the dryer section softens residual acrylic resins, causing polymer transfer onto drying can surfaces. Deposited resins pick fibers from the wet web, creating holes, localized caliper variations, and web breaks.
Machine downtime increases proportionally with the accumulation rate of tacky residues.
| Particle Size Class (μm) | Screening Classification | Deposition Mechanism | Mass Fraction (% Total Resin) | Machine Hazard Level |
|---|---|---|---|---|
| Greater than 150 | Macro-Sticky Reject | Screen Slot Clogging | 62.4 | Low (Captured by Screens) |
| 50 to 150 | Screen Accept / Micro-Sticky | Felt Infiltration and Deposition | 21.8 | Critical (High Runnability Risk) |
| 1 to 50 | Colloidal Suspension | White Water Agglomeration | 12.3 | Moderate (Accumulative Risk) |
| Less than 1 | Dissolved / Solubilized Polymer | Chemical Oxygen Demand Load | 3.5 | Low (Effluent Risk) |
| Total Suspended Mass | Combined Residue Population | System-Wide Deposition | 100.0 | Summary Baseline |
Effluent treatment systems experience elevated Chemical Oxygen Demand levels when water-soluble polymer fractions dissolve into process streams. Dissolved acrylic resins resist mechanical settling, requiring chemical coagulants such as polyaluminum chloride or cationic polymers to force precipitation prior to biological treatment.
Higher dispersion coat weight increases total reject mass and lowers clean pulp yield despite maintaining constant base sheet pulp quality.
Incomplete dispersion breakup during stock preparation contaminates the recycled water circuit, forcing emergency downtime and wet-end fabric replacement across downstream paper mills.

Calculus
Determining the net economic value of repulped dispersion substrates requires a complete mass balance across input tonnage, moisture variations, and reject losses. Paper mills buy raw stock by gross weight but derive commercial value exclusively from clean, usable cellulose recovered post-screening. Non-cellulosic barrier coatings represent paid mass that converts into process waste during disintegration.

Mass Balance and Fiber Recovery Arithmetic
Dry mass calculations track total yield by isolating bone-dry fiber mass from barrier polymer weights. Take a 100-tonne commercial lot of dispersion-coated folding boxboard with a nominal grammage of 365 grams per square meter. The base board accounts for 350 grams per square meter, while the acrylic barrier dispersion contributes 15 grams per square meter.
Delivery moisture content measures 7 percent across the shipment.
Gross dry mass equals 93 metric tons after removing 7 metric tons of moisture weight. The acrylic coating accounts for 3.84 percent of the dry sheet mass, equaling 3.57 metric tons of non-fiber material. The remaining 89.43 metric tons represents total cellulosic furnish.
The 88 percent dry mass fiber recovery figure assumes a base board moisture content of 7 percent and a coat weight of 12 grams per square meter. An increase in coating density to 22 grams per square meter reduces recovery to 81 percent.
Standard pulping and Somerville screening yields an 8 percent total dry reject rate. Dry reject mass equals 7.44 metric tons. Furnace calcination confirms that synthetic polymer flakes account for 3.30 metric tons of this reject mass, while bound, unseparated wood fibers account for the remaining 4.14 metric tons.
Net usable fiber recovered from the initial 100-tonne lot equals 85.29 dry metric tons.

Financial Yield Modeling for Recycled Furnish
Substrate cost analysis incorporates pulping losses, effluent disposal charges, and virgin fiber replacement pricing. Assume an initial delivered stock price of 850 US dollars per gross metric ton landed at the mill door. The raw substrate purchase cost for the 100-tonne lot equals 85,000 US dollars.
Dividing gross expenditure by the 85.29 dry metric tons of recovered usable fiber yields a true pulp cost of 996.60 US dollars per dry metric ton of recovered furnish.
Process waste handling introduces secondary operational expenses. Disposing of 7.44 metric tons of wet screening rejects incurs landfill or incineration charges at 120 US dollars per metric ton, adding 892.80 US dollars to the batch run cost. Effluent treatment chemicals required to settle suspended colloidal resins cost an estimated 15 US dollars per metric ton of processed stock, adding 1,500 US dollars.
Total production cost reaches 87,392.80 US dollars for the batch.
- Coat weight ratio determines the proportion of non-cellulosic material entering the hydrapulper per metric ton.
- Crosslinking density controls chemical resistance to water penetration during mechanical agitation.
- Rotor shear rate governs the physical breakdown velocity of the polymer film into discrete particles.
The final effective fiber cost equals 1,024.65 US dollars per dry metric ton of usable furnish. Disintegration yield loss and waste processing inflate raw material cost by 20.5 percent relative to the initial purchase price. Yield loss inflates cost.
Standard packaging purchasing contracts specifying Class A Aticelca certification allow buyers to issue immediate debit notes when laboratory fiber accept yield falls below 85 percent.
Calculating stock cost on raw gross tonnage without accounting for reject screening loss overstates usable fiber volume and skews converting profit margins.

Conformance
Market acceptance of dispersion-coated packaging depends on certified alignment with standardized recyclability schemes. Industrial paper mills establish rigid quality criteria for incoming secondary fiber stock to protect machine efficiency. Mill certificates must explicitly detail disintegrability parameters alongside standard physical sheet measurements.

Certification Standards and Laboratory Qualification
Testing protocols established by European paper industry associations define precise laboratory workflows for disintegrability evaluation. The Aticelca 501/19 evaluation system categorizes substrates into four distinct recyclability classes based on fiber yield, coarse reject percentages, and macro-sticky formation. Class A status requires a minimum fiber accept yield of 85 percent and total coarse rejects below 1.5 percent after 10 minutes of pulping.
Certification testing utilizes standard laboratory pulpers operating under controlled temperature, consistency, and rotor speed parameters. Third-party testing laboratories issue formal test dossiers validating substrate compliance before commercial release. Re-certification occurs when paper mills alter coating formulations, coat weights, or base sheet furnish compositions.
| Standard / Framework | Classification Grade | Minimum Fiber Accept Yield (%) | Maximum Coarse Reject Limit (%) | Macro-Sticky Limits (mm²/kg) |
|---|---|---|---|---|
| Aticelca 501/19 | Class A+ (Superior) | 90.0 | 1.5 | Less than 2,000 |
| Aticelca 501/19 | Class A (Standard) | 85.0 | 5.0 | Less than 5,000 |
| CEPI Recyclability Guideline | Pass Threshold | 80.0 | 15.0 | Not Specified |
| PTS-RH 021/97 | Category A (Recyclable) | 80.0 | 10.0 | Visual Pass Benchmark |
| Extended Producer Responsibility | Premium Tariff Level | 92.0 | 2.0 | Zero Deposition Allowed |

Supply Contract Specifications and Rejection Thresholds
Commercial procurement contracts translate laboratory yield metrics into binding quality criteria for delivered reels. Purchasing specifications require mill certificates to state average Somerville screen reject percentages for each production tambour. Rejection clauses execute automatically when delivered lots fall below certified disintegration yield minimums.
Extended Producer Responsibility regulations impose variable financial tariffs on packaging substrates based on certified recyclability metrics. Substrates achieving high fiber accept yields and low sticky creation earn reduced compliance fee rates. Substrates generating high reject volumes incur financial penalties, directly increasing total packaging unit costs for brand owners.
The industry continues to debate whether standardized disintegration yield metrics should prioritize raw fiber volume recovery or the physical energy expenditure required to break complex acrylic barrier lattices during pulping.




