Compare recyclable-packaging options by the cost of delivering accepted, protected product. A cheaper purchased pack can create a higher production cost if it adds scrap, changeover work or product loss; a higher material price can also be offset by documented savings elsewhere.

Separate paperboard sleeve, clear tray, film lid and blank label on a table
Compare all parts needed for an equivalent functioning package, rather than only the most visible component.

Define the same job for both alternatives

Write a comparison boundary before collecting quotes. State the product, protected quantity, distribution conditions and acceptance criteria. Keep the comparison period and product mix consistent. If one option needs an additional insert, label or outer pack, include it in that option’s bill of materials.

Cepi’s guidance places product protection alongside recycling compatibility and points readers toward national systems. That is a useful boundary for a paper-packaging alternative: do not assign a recycling benefit without the appropriate route evidence, and do not remove protection requirements to make a candidate appear cheaper.

The worksheet below is a decision model. It does not supply market prices, typical premiums or assumed machine performance.

Build a cost record that a colleague can audit

Compare recurring production costs on the same accepted-output basis. Keep one-time conversion work visible beside that comparison. If you spread conversion costs over a forecast volume, state the volume and time period rather than presenting the result as an inherent material property.

Cost or evidence item Existing construction Proposed construction Source to attach
Whole-pack materials Actual usage and delivered price Equivalent scope and commercial terms Bill of materials, quote or invoice
Normal conversion work Labor, utilities and routine consumables Measured or trial-based assumptions Batch and production records
Rejects and product losses Observed loss on the defined boundary Trial result or explicit unresolved assumption Counts and disposition records
Changeover and cleanup Actual time and material issued Trial observation for relevant formats Changeover record
One-time work Separate from recurring total Tooling, engineering, trials and qualification Approved project scope
End-of-life evidence Route and assessment status Same market-specific check Dated primary evidence

Do not turn an unknown into zero. An untested scrap rate should remain a scenario input with an owner, not a claimed saving.

Copyable cost-per-accepted-pack worksheet

Copy these blank tables for the same product-protection task and period. Record the currency and each quantity unit. Keep mutually exclusive cost inputs so that material, labor or loss already charged in one row is not added again elsewhere.

Comparison boundary Existing construction Proposed construction
Product, pack revision and protection / acceptance rule ______ ______
Batch or comparison period and product mix ______ ______
Currency and cost view: accounting or incremental cash ______ ______
Material quantity units and stock-adjustment basis ______ ______
Evidence revision / calculation date ______ ______
Mutually exclusive recurring input Existing construction Proposed construction Evidence / units
M: packaging material consumed, including its setup/reject usage once ______ ______ Quantity × delivered rate; currency ______
P: normal conversion labor, utilities and consumables ______ ______ Hours or quantity × stated rate; currency ______
X: additional changeover / cleanup not already in M or P ______ ______ Hours or quantity × stated rate; currency ______
L: additional product-loss / rework cost not already charged above ______ ______ Recorded loss basis; currency ______
E: selected disposal fee, if included in this boundary ______ ______ Matched-period fee record; currency ______
Calculation Existing construction Proposed construction
Recurring total R = M + P + X + L + E R_old = ______ R_new = ______
Accepted output N in the same period N_old = ______ packs N_new = ______ packs
Recurring cost per accepted pack C = R ÷ N C_old = ______ / pack C_new = ______ / pack
Recurring difference per accepted pack Reference C_new − C_old = ______ / pack
One-time conversion work K, outside R ______ ______
Forecast accepted volume V and allocation period, if used ______ packs; period ______ ______ packs; period ______
Optional one-time allocation per pack A = K ÷ V A_old = ______ / pack A_new = ______ / pack
Optional scenario cost per pack S = C + A S_old = ______ / pack S_new = ______ / pack
Optional scenario difference Reference S_new − S_old = ______ / pack
Unresolved input / source missing Could it change the choice? Evidence or next action Owner / review date
______ ______ ______ ______

Use M after documented returns and stock adjustments. If actual material consumption already includes setup offcuts and rejected packaging, those amounts stay in M; do not add them again to X or L. Use only additional changeover time in X when P excludes it. Product contents lost in a reject may belong in L, while the same reject’s packaging remains in M. State those boundaries in the evidence column.

Leave unknowns blank; enter zero only when the boundary and evidence support it. Calculate C only when N is greater than zero and the optional allocation A only when V is greater than zero. Keep the selected fee E out of other rows. K stays outside recurring R even when you show its separate forecast-volume allocation. A negative new-minus-old difference indicates a lower modeled cost on this stated basis, not a measured saving.

Count material that never becomes an accepted pack

Material consumption includes startup, setup and rejects as well as accepted output. Reconcile issued material with returns and loss where practical. State whether an invoice price already includes freight or other charges before adding those costs again.

Illustrative issued roll, returned stock, setup offcuts, rejected packaging and accepted packaging each have separate blank kilogram entries; net issued is gross issued minus returned
Separate issued and returned stock from setup offcuts, rejected packaging and accepted packaging. The blank mass record uses one material unit; it supplies no yield or measured quantities.

Syntegon’s flow-wrap article connects process stability with fewer rejected products and explains that alternative films can require sealing adjustments. That supports investigating conversion losses. It does not establish a scrap percentage or a retrofit cost for your operation.

Reconcile material across accepted output and process losses; the diagram contains no assumed yield.
Reconcile material across accepted output and process losses; the diagram contains no assumed yield.

Use the material ledger to locate usage, and the accepted/loss diagram to define the output boundary. Neither supplies a yield benchmark. If the line reports rejected packs but the material record reports roll mass, keep the units separate until you have a documented conversion. Do not compare one option per purchased unit and the other per accepted unit.

Test the assumptions that could reverse the choice

Start with the assumptions that are both uncertain and influential. A trial may resolve material usage or restart losses. A revised supplier scope may resolve tooling cost. A collector’s instructions may show that the claimed recycling route does not apply to the package’s discard condition.

Run a lower-volume scenario if the business case depends on spreading conversion work over future demand. Separate releasable cash savings from capacity that becomes available but is not yet sold. A reduction in operator attention may be valuable without producing a payroll reduction; describe what the team can do with that time.

Record a conditional decision: proceed, revise the design, gather missing evidence or retain the existing construction. List the evidence required before the choice changes. The paper recyclability guide helps test route assumptions; the EPR record isolates the reporting and fee calculation. Both sit within recycling economics.

Methods and limits

The model is original editorial guidance based on the cited material and process explanations. It is not a lifecycle assessment, a supplier quote or a forecast of recycling revenues. No costs, yields or savings have been measured by this publication. Checked October 2026.