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Research libraryCarbon per Garment

Chapter 01 of 14 · Part I · Draft web edition

Carbon per garment is an accounting discipline, not a slogan

A garment number becomes decision-ready only when its boundary, function, evidence and intended use are explicit.

Sections
6
Exhibits
4
Minutes
24
Sources
16
EX 02 · Materials and manufacturing to Shirt at factory gate: 0.3 kg per defined cotton shirt reference flow

The cloth is woven from this chapter's 4 exhibits: each weft is one exhibit's own data, normalised; each warp group is a section. The probe reads the exhibit's own value where it crosses. Procedural visualisation, not a measurement.

The chapter as a draft: 6 sections, 3 exhibit wefts, one shuttle.

Lead exhibit · 02Material flowillustrativeA reference shirt cannot acquire a footprint before its boundary is declared
Defined cotton shirtMaterials and manufactu…Shirt at factory gateUse and end-of-life sce…

Read-outDefined cotton shirt to Materials and manufacturing: 0.3 kg per defined cotton shirt reference flow

Method and source

Illustrative boundary model using the 250 g medium-size cotton shirt baseline in S31, expressed as 0.25 kg. Each link carries the same shirt-equivalent reference flow to preserve the denominator. This is not a physical mass balance and assigns no emissions. Losses, added materials, energy, freight, use and disposal require separate activity data and factors before calculation.

Unit: kg per defined cotton shirt reference flow. Status: illustrative. Sources: S31. Illustrative figures are teaching examples, not measured factory results.

The chapter's warpBar: share of the reading · square: an exhibit

Section 1.0 · Opening · 1 min · no exhibit of its own · one movement Go to section ↓

Overture · 1 min

Carbon per garment is an accounting result, not an intrinsic property that can be read from a fibre label or a factory name. The result is constructed from a declared life cycle boundary, a defined garment and function, physical activity data, dated emission factors and explicit allocation rules.[S01][S23] Change any of those choices and the number can change without any change on the production line. A useful footprint therefore begins with an evidence trail that another practitioner can inspect, not with a marketing adjective. Green Future Tech Limited (GFT) applies a simple sequence to its Cameroon textile programme: establish the account, use it to reduce emissions, and permit a public claim only after the evidence supports the wording. This chapter defines that discipline. Later chapters develop the detailed calculations, but the governing principle is already clear: a number that cannot explain its own scope cannot guide a decision.

¶ 01 · 2 sources

S01S23

1.14 min · 3 sub-steps · 2 exhibits

A number without a boundary is not a footprint

Exhibit 01Line boardsourcedFive fields make a garment footprint intelligible

Read-out · sourcedBoundary: Declared. Name included and excluded life cycle stages.

Method and source

Sourced synthesis of full life cycle coverage in S01, the single climate impact category in S05, greenhouse gas metric assessment in S11, and activity data, emission factor and GWP disclosure in S23. The five fields are an organising device, not an additional reporting standard.

Unit: required accounting declarations. Status: sourced. Sources: S01, S05, S11, S23.

A footprint must first answer the question, "Which emissions belong to this garment, over which period, for what function?" The GHG Protocol Product Standard covers raw materials, manufacturing, transportation, storage, use and disposal.[S01] A result limited to spinning, dyeing or garment assembly may be useful for supplier exchange or process control, but it is not a full life cycle result. Its name must preserve that limitation. "Cradle-to-gate carbon per defined shirt" and "full life cycle carbon per defined shirt" are different statements, not two wordings for the same calculation.[S01][S23]

The boundary is more than a list of stages. It also determines whose electricity is included, whether inbound and outbound freight appear, how packaging and waste are treated, and whether consumer care and final disposal are measured or modelled.[S01][S23] A factory can calculate its own utility emissions with care and still omit most of the garment system if purchased fabric, subcontracted wet processing or product use sit outside the account. Conversely, adding a supplier's cradle-to-gate factor to a full life cycle factor for the same material would introduce emissions twice. Boundary control therefore precedes arithmetic.

¶ 02 · 2 sources

S01S23

A partial account is not necessarily a weak account. A mill may need a gate-to-gate model to manage a boiler, while a buyer may need a cradle-to-gate record for a purchased fabric. The error lies in allowing the result to migrate into a wider claim without adding the missing stages. The GHG Protocol distinguishes cradle-to-gate factors, which stop at the supplier's point of sale, from life cycle factors that continue through subsequent stages.[S23] That distinction gives each module a proper use and prevents a convenient supplier number from becoming an unsupported garment claim.

¶ 03 · 1 source

S23

1.2 Five fields make the result intelligible

1.2

Before reviewing a total, a reader should be able to inspect five fields: the boundary, the functional unit, the gases and global warming potential (GWP) convention, the activity data, and the emission factors. ISO 14067 confines a product carbon footprint to climate change, while Scope 3 guidance requires transparency about activity data, factors and GWP sources.[S05][S23] Exhibit 1 turns those requirements into a reading test for any garment figure.[S01][S05][S11][S23]

¶ 04 · 4 sources

while Scope 3 guidance requires transparency about activity dataS05, S23

Exhibit 01

S05S23S01S11

These fields expose different failure modes. An unclear boundary hides omissions. An undefined functional unit hides differences in garment mass, quality or service. An unrecorded GWP convention prevents consistent conversion of non-CO2 gases into CO2e.[S11][S23] Untraceable activity data prevent the reader from returning to a meter, invoice or supplier record. An undated factor can attach the wrong geography or period to an otherwise sound physical measurement. Precision in the final decimal place cannot repair any of these defects.

¶ 05 · 2 sources

An unrecorded GWP convention prevents consistent conversion of non-CO2 gases into CO2eS11, S23

S11S23

The functional unit deserves particular restraint here. A kilogram of fabric, one finished garment and one wear are not interchangeable denominators. They support different decisions and require different reference flows.[S01][S23] Moreover, the GHG Protocol Product Standard notes that its primary purpose is tracking a product's greenhouse gas inventory and reductions over time, whereas comparing two or more products for labels or performance claims requires additional methodological prescription on allocation rules and data sources.[S0101] The detailed functional-unit and comparison rules follow in the next chapters. For this opening argument, the requirement is simpler: state exactly what the denominator represents and do not allow it to change during comparison.

¶ 06 · 3 sources

S01S23S0101

1.3 A reference shirt demonstrates why scope comes first

1.3

Consider a defined cotton shirt with a baseline mass of 250 grams, the reference used in a comparative T-shirt life cycle study.[S31] That mass identifies a reference flow; it does not supply an emission factor, a cotton yield, a factory energy record or a downstream care scenario. Exhibit 2 carries the same illustrative shirt reference through a boundary map without assigning any emissions. It is deliberately not a physical cotton mass balance, because losses, trims and other inputs remain to be measured.[S23][S31]

¶ 07 · 2 sources

Consider a defined cotton shirt with a baseline mass of 250 gramsS31

Exhibit 02

S31S23

The exhibit shows why a footprint cannot be inferred from garment mass alone. The upstream module needs material and energy evidence. The factory-gate handover needs a clear statement of what the supplier included. The downstream module needs scenarios for distribution, laundering, service life and disposal, each labelled as observation or assumption.[S01][S23] Only then can the modules form a full life cycle account without gaps or repetition.

¶ 08 · 2 sources

S01S23

1.4 Carbon is one environmental account, not the whole sustainability account

1.4

ISO 14067 addresses climate change alone and excludes social, economic and other environmental impacts from its scope.[S05] A low carbon result therefore cannot establish low water use, acceptable effluent, low toxicity, fair work or garment durability. Nor can a high result prove the opposite. Carbon accounting earns its place by answering one question well, not by absorbing every question into a single score.

¶ 09 · 1 source

S05

This limitation changes how claims should be written. "Lower CO2e per defined garment under the stated boundary" is a testable proposition if the evidence agrees. "Sustainable garment" is a much broader proposition that the carbon account cannot support on its own.[S05][S32] GFT's carbon workstream therefore sits beside, rather than replaces, the operating records for water, energy, materials, quality and waste in its Cameroon textile programme.

¶ 10 · 2 sources

S05S32

1.52 min · 1 sub-steps · 1 exhibit

Corporate and product accounts answer different questions

Step 1 of 7Organisational boundary

Exhibit 03 · sourcedOne garment creates two linked carbon accounts

OrganisationalboundaryScopes 1, 2 and 3Corporate inventoryDefined garment andfunctionProduct life cyclestagesProduct footprintReconcile sharedevidence
OrganisationalboundaryScopes 1, 2 and 3Corporate inventoryDefined garment andfunctionProduct life cyclestagesProduct footprintReconcile shared evidence

Organisational boundary

Organisational boundary. Starting point. Leads to Scopes 1, 2 and 3. · sourced

An organisational inventory and a product footprint share physical evidence, but they do not serve the same decision.

Scopes 1, 2 and 3

Scopes 1, 2 and 3. From Organisational boundary. Leads to Corporate inventory. · sourced

Corporate inventory

Corporate inventory. From Scopes 1, 2 and 3. Leads to Reconcile shared evidence. · sourced

Defined garment and function

Defined garment and function. Starting point. Leads to Product life cycle stages. · sourced

Product life cycle stages

Product life cycle stages. From Defined garment and function. Leads to Product footprint. · sourced

Product footprint

Product footprint. From Product life cycle stages. Leads to Reconcile shared evidence. · sourced

Reconcile shared evidence

Reconcile shared evidence. From Corporate inventory, Product footprint. End point. · sourced

Method and source · Exhibit 03

Sourced process synthesis. S04 governs the corporate inventory, S02 its upstream and downstream Scope 3 coverage, S01 the product life cycle account, and S23 the calculation methods and evidence descriptions. Reconciliation compares shared activities, periods and boundaries; it does not assert that corporate and product totals are interchangeable.

Unit: accounting architecture. Status: sourced. Sources: S01, S02, S04, S23.

1.5 · the bodyExhibit 03 above; its figures are illustrative where marked.

An organisational inventory and a product footprint share physical evidence, but they do not serve the same decision. The corporate account reports emissions within an organisational and value chain boundary for a reporting period.[S02][S04] The product account follows a defined good through its life cycle and expresses the result against a functional unit.[S01] One asks what the organisation is responsible for managing. The other asks what burden attaches to the garment system being designed, purchased or sold.

The GHG Protocol makes this separation explicit: its Scope 3 standard accounts at corporate level, while its Product Standard accounts at individual product level.[S02] Treating the corporate total divided by annual units as the footprint of every garment would conceal product mix, sourcing and life cycle differences. Treating one garment study as the corporate inventory would omit other products, sites, activities and relevant Scope 3 categories. The accounts must meet, but neither can substitute for the other.

¶ 02 · 1 source

its Scope 3 standard accounts at corporate levelS02

S02

1.6 Shared activity enters through two controlled routes

1.6

Exhibit 3 shows the required architecture. Organisational Scopes 1, 2 and 3 form one route. Product definition and life cycle stages form the other. A reconciliation bridge then compares shared activities without assuming that the two totals should be numerically identical.[S01][S02][S04][S23]

¶ 03 · 4 sourcesExhibit 03

S01S02S04S23

The bridge is a control, not a forcing function. A garment factory's purchased electricity may appear in its Scope 2 inventory and, after allocation, in a shirt's cradle-to-gate footprint.[S01][S04] The same kWh must retain one identity across both records. If the corporate inventory reports the full site period while the product model covers one order, the reconciliation must explain the difference in period and denominator rather than adjust one total until it resembles the other.

¶ 04 · 2 sources

A garment factory’s purchased electricity may appear in its Scope 2 inventory andS01, S04

S01S04

Scope 3 calculation guidance supplies methods by corporate category, including purchased goods, transport, use and end-of-life.[S02][S23] Those categories provide a systematic completeness check for the organisation. They do not, by themselves, define a product's functional unit, allocation between co-products or equivalent garment performance. A category total cannot simply be relabelled as a product life cycle assessment. The product model needs its own goal and scope, while the corporate model needs assurance that every relevant category has been screened.

¶ 05 · 2 sources

Scope 3 calculation guidance supplies methods by corporate categoryS02, S23

S02S23

This separation also clarifies responsibility. The GHG Protocol Corporate Standard distinguishes greenhouse gas accounting from greenhouse gas reporting: accounting governs the recognition and consolidation of emissions and links data to specific operations, sites, geographic locations, business processes and owners, while reporting governs how that consolidated information is presented to users.[S0102] In an apparel business, the sustainability team may own the corporate inventory, product engineers may own the garment model, and procurement may own supplier evidence, but all three must use compatible identifiers for sites, suppliers, materials, orders and periods.[S04][S0102] GFT's discipline is therefore administrative as much as mathematical: a carbon figure needs an owner, a version and a route back to source activity.

¶ 06 · 2 sources

S0102S04

1.73 min · 2 sub-steps · read with a related exhibit

Scope 3 prevents a factory from outsourcing its carbon story

Related · chapter 119 paragraphs step it

Related exhibit 51 · chapter 11LayerssourcedAn electricity evidence stack runs from meter to contractual instrument
Disclosure andproduct allocationDual Scope 2 corporate reportScope 3 Category 3 fuel and l…Accepted-garment allocation b…Contractual andfactor governanceEight Scope 2 quality criteri…Dated IEA location-based grid…Residual mix or supplier-spec…Boundary separationGeneration-only kWh factorTransmission and distribution…Well-to-tank upstream fuel fa…Physical capture andreconciliationSub-metered line and utility…Self-generated solar PV and e…Utility invoices and diesel t…

Read-outDisclosure and product allocation: Dual Scope 2 corporate report, Scope 3 Category 3 fuel and loss ledger, Accepted-garment allocation bridge

Method and source

Accounting architecture synthesised from GHG Protocol Scope 2 Guidance (S03), IEA Emissions Factors 2026 (S14), UK DESNZ conversion factors 2026 (S20) and Scope 3 calculation guidance (S23). Separates physical metering, grid generation factors, transmission and distribution losses, upstream fuel-cycle burdens and market-based contractual quality criteria.

Unit: . Status: sourced. Sources: S03, S14, S20, S23.

Read this exhibit in its chapter ↗
1.7 · Introduction · paragraph 1 of 9

A factory does not remove emissions from its account by purchasing a material or subcontracting a process. The GHG Protocol Scope 3 framework covers upstream and downstream activities across 15 categories, providing a structure for screening emissions beyond owned operations.[S02] For an apparel business, that means the evidence plan must look beyond the sewing floor to purchased fibre, yarn, fabric and trims, outsourced processing, freight, waste, product use and disposal where relevant.[S02][S08][S23]

The word "relevant" matters. Scope 3 accounting does not require every activity to receive the same depth of measurement at the outset. The calculation guidance recommends an initial screen using less specific data, followed by more precise work on significant emissions, reduction opportunities and business priorities.[S23] This is a disciplined allocation of evidence effort. A small administrative purchase may remain a secondary-data estimate while a dominant fabric input justifies supplier-specific activity data and closer review.

1.8 Apparel hotspots make purchased evidence an operating requirement

Apparel and footwear guidance identifies significant value chain emissions and frequent hotspots in fibre production, yarn preparation, dyeing and finishing.[S08] A cut, make and trim operation can therefore have careful utility records and still lack evidence at the stages that drive much of the garment result. The correct response is not to assume a universal hotspot percentage. It is to screen the actual bill of materials and process route, then test where better evidence would change the decision.[S08][S23]

This turns procurement into part of the measurement system. A purchase order identifies what was bought, but a carbon record also needs the supplier, product specification, quantity, production period and appropriate cradle-to-gate factor.[S23] Where a supplier provides a footprint, the buyer needs its boundary, allocation method, data sources, GWP convention and assurance status before using it. A PDF attached to an email is not sufficient if those fields are absent.

Supplier-specific evidence is not automatically superior. GHG Protocol guidance warns that supplier data can be less accurate than an industry average when granularity, source reliability or allocation is weak.[S23] A precise number calculated from an unrepresentative month, an unclear product allocation or an unrecorded proxy may be less useful than a transparent industry estimate. The evidence plan must assess fitness for the intended decision rather than award credibility on the basis of provenance alone.

1.9 Data requests should build capability rather than shift ambiguity

UNIDO's 2010 guide for garment, footwear and furniture suppliers anticipated growing pressure on developing-country suppliers to address their carbon footprints through business relationships.[S21] The practical lesson for a Cameroon programme is not to reproduce a buyer questionnaire and pass it upstream unchanged. It is to make the request physically intelligible to the spinner, dyer, logistics provider or garment line that holds the source record.

A useful request starts with quantities the supplier already controls: fuel used, electricity purchased, material received, accepted output, waste and transport work. It then asks for the factor and method needed to convert those quantities into CO2e.[S23] Where the supplier cannot respond, the buyer can use a labelled proxy from screening data and record who will replace it, by which review gate. That approach separates a temporary data limitation from a permanent exemption.

The same approach prevents double counting between commercial boundaries. If a fabric supplier's cradle-to-gate result already includes inbound yarn transport, the garment buyer must not add that leg again as an independent purchased-goods block. If a subcontractor reports only gate-to-gate energy, the remaining material and upstream inputs still need to be represented.[S23] Scope 3 therefore does more than enlarge the inventory. It forces each handover to state exactly what evidence accompanies the product.

Interlude · the cloth half-woven

4 exhibits carry this chapter's argument.

Woven: sections 1.0 to 1.7Still to weave: 1.10 to 1.14

  1. 01Five fields make a garment footprint intelligibleKey figures
  2. 02A reference shirt cannot acquire a footprint before its boundary is declaredMaterial flow
  3. 03One garment creates two linked carbon accountsFlow
  4. 04Global fibre volume increased before any emissions calculationExhibit
Hover or focus an exhibit to light its weft; select it to jump to it.
Key figures from chapter 07 · Exhibit 33Key figuressourcedDaily capture joins carbon to the existing operating record across six shift field groups
  • kWh / shiftPurchased grid and direct-line electricityMain revenue meter plus feeder sub-meters by line and utility room (S20, S0704)
  • L, kg or MJOn-site fuel, steam and self-generationBoiler fuel, steam flow, genset diesel and self-generated solar kWh (S20, S0701)
  • A-grade piecesStarted and accepted good unitsCut bundles loaded, first-pass accepted units and final shipped count (S23, S24)
  • pieces and SAMDefects, rejects and rework SAMTagged by defect code, station and rework standard minutes (GFT programme, S23)
  • min / shiftLine operating and downtime minutesSeparates productive running time from idle baseload draw (GFT programme, S20)
  • kg / batchSegregated process waste and leaksCutting offcuts, rejected seconds, carton scrap and refrigerant logs (S20, S0702)

Read-outPurchased grid and direct-line electricity: kWh / shift. Main revenue meter plus feeder sub-meters by line and utility room (S20, S0704)

Method and source

Sourced from UK DESNZ and IEA activity-data requirements (S14, S20), GHG Protocol Scope 3 allocation guidance (S23), US EPA stationary, fugitive and electricity guidance (S0701, S0702, S0704) and GFT programme design.

Unit: daily operational data schema. Status: sourced. Sources: S14, S20, S23, S0701, S0702, S0704.

Read this exhibit in its chapter ↗

1.103 min · 2 sub-steps · read with a related exhibit

Cameroon needs an operational baseline, not a borrowed label

Step 1 of 3Intro

Related exhibit 25 · chapter 05Decision mapsourcedA cotton evidence register separates activity, factor and counterfactual priorities
Standardise method rulesCollect local primary evidencefirstRetain documented screeningdefaultsVerify regional boundary conditionsProxy distortion risk (0 to 10) →Sensitivity of lint CO2e footprint (0 to 10) →Lint yield per haSynthetic N rate and…Irrigation water and…Soil N2O climate tier…Ginning energy and ou…Co-product allocation…Land-use change and S…GWP version and gas s…

Read-outLint yield per ha: Proxy distortion risk (0 to 10) 8.5, Sensitivity of lint CO2e footprint (0 to 10) 9.2. Quadrant: Collect local primary evidence first

Method and source

Sourced governance classification mapped on a 0 to 10 decision grid. The eight register fields are drawn from IPCC metric and soil rules (S11, S0501), ecoinvent geographic proxy limits (S16), Watson and Wiedemann cotton LCA sensitivity review (S26) and FAO nitrogen guidance (S29). Coordinates represent analytical priority for primary-data replacement in GFT's Cameroon programme, not measured emissions.

Unit: priority score from 0 (low) to 10 (high). Status: sourced. Sources: S11, S16, S26, S29, S0501.

Read this exhibit in its chapter ↗

1.10 · Introduction

Cameroon’s industrial opportunity does not come with a pre-existing garment carbon factor.

Exhibit 25, chapter 05: Lint yield per ha

1.11 · The production period belongs inside the baseline

Energy conditions also make vintage essential.

Exhibit 25, chapter 05: Lint yield per ha

1.12 · A baseline is a repeatable operating record

The practical starting unit is not a polished annual report.

Exhibit 25, chapter 05: Synthetic N rate and form

1.10 · the bodyThe film above follows these sub-steps.

Cameroon's industrial opportunity does not come with a pre-existing garment carbon factor. The inherited sector evidence records about 95 percent of cotton fibre exported raw and about 5 percent processed locally, with an industrialisation target of 50 percent local processing.[R06] Those figures describe the structure of the cotton sector in the inherited register, whose original publication date was not recorded. They are not measurements of carbon intensity, and they do not demonstrate that local processing will automatically lower emissions per garment.

¶ 01 · 1 source

with an industrialisation target of 50 percent local processingR06

Related · Exhibit 50 · chapter 10

R06

Local production changes the system that must be measured. It can alter transport legs, electricity supply, thermal processes, yields, co-products and the division of activities between organisations. The carbon result depends on those actual conditions, not on the location claim itself. A footprint assembled from an overseas fibre average, an unspecified grid factor and a generic garment study would be a screening model with proxies, not an operational Cameroon baseline.[S23]

¶ 02 · 1 source

S23

1.11 The production period belongs inside the baseline

1.11

Energy conditions also make vintage essential. The International Energy Agency country profile for Cameroon notes that electrification is relatively high for Central Africa, with 54 percent of the population having access to electricity while consumption remains low.[S09] Meanwhile, in January 2025, the World Bank described Cameroon's hydropower and solar development as part of an active shift substituting diesel-based generation to lower costs and cut carbon emissions.[S28] Reading those two public records side by side shows why source vintage matters: a country profile that retains an older access figure and a 2025 report on grid and solar investment describe different moments in a changing power system, and neither supplies a site-specific factor for an individual factory.[S09][S28] A garment baseline must record when and where production occurred, which electricity and fuels were used, and which dated factor version converted those activities into CO2e.[S09][S23][S28]

¶ 03 · 3 sources

with 54 percent of the population having access to electricity while consumption remains lowS09

S09S28S23

An old national average should not be attached to a new production period merely because it is available. Equally, a newer factor should not be used to rewrite history without a recalculation rule. Scope 3 guidance requires significant data-quality improvements to trigger base-year recalculation where they materially change emissions estimates.[S23] The account therefore needs both an activity year and a factor lineage. Without them, a method update can masquerade as an operational reduction.

¶ 04 · 1 source

Scope 3 guidance requires significant data-quality improvements to trigger base-year recalculation where they materially…S23

S23

The baseline must also separate what happened from what was assumed. Metered electricity is observed activity. A supplier's missing fuel record replaced with an industry average is estimated activity. A future consumer-care pattern is a scenario. These inputs can coexist in a screening model, but they cannot carry the same claim status.[S23] Keeping them distinct allows the next data collection round to improve the account without pretending that the first model was measured end to end.

¶ 05 · 1 source

S23

Note · 1 sourceReplay in the film

S23

1.12 A baseline is a repeatable operating record

1.12

The practical starting unit is not a polished annual report. It is a controlled record joining production, procurement and utilities for the same period. Fabric and trim receipts identify purchased inputs. Meters and fuel records identify site activity. Accepted output identifies the production denominator. Supplier documents identify upstream boundaries. Each record carries an owner and a version so that corrections remain visible.[S04][S23]

¶ 06 · 2 sources

S04S23

A baseline pilot should follow one representative garment through the complete method before expanding to every style. That pilot exposes mismatched units, missing stages and allocation problems while they are still inexpensive to correct. It also establishes which proxies dominate the result and therefore deserve supplier requests or meter investment first.[S23] Scaling a spreadsheet before resolving those issues would multiply confusion rather than produce coverage.

¶ 07 · 1 source

S23

GFT's Cameroon textile programme already provides the operating context for this work through feasibility, performance-management system design and digital strategy. The carbon layer adds factors, gas conventions, life cycle boundaries and claims control to the production record. It does not presume a measured saving or a commercial advantage. Its first deliverable is a baseline that can survive recomputation and show management where action would matter.

¶ 08

1.133 min · 7 paragraphs · 1 exhibit

Absolute emissions and intensity must travel together

A lower footprint per garment does not necessarily mean lower total emissions. Absolute emissions equal production volume multiplied by emissions per unit when the boundary and product definition are held constant. If volume rises faster than intensity falls, the total increases. Apparel target guidance recognises both absolute contraction and physical intensity approaches, with intensity translated into absolute terms rather than treated as an end in itself.[S08] A serious operating review therefore retains total CO2e beside CO2e per accepted garment and, where the question concerns service, CO2e per wear.[S08][S23]

¶ 01 · 2 sources

A serious operating review therefore retains total CO2e beside CO2e per accepted garment andS08, S23

Related · Exhibit 56 · chapter 12

S08S23

The need for both measures is visible before any emissions calculation. Textile Exchange reports that global fibre production increased from 125 million tonnes in 2023 to 132 million tonnes in 2024 across apparel, home textiles, footwear and other applications.[S07] That is an increase of 7 million tonnes, or 5.6 percent derived as 7 divided by 125.[S07] It is not an emissions growth estimate, because fibre mix, geography and factors would need separate evidence. It does show why a production system cannot infer absolute climate progress from efficiency alone.

¶ 02 · 1 source

…global fibre production increased from 125 million tonnes in 2023 to 132 million tonnes…S07

S07

Exhibit 4 preserves the two reported observations without converting them into CO2e.[S07]

¶ 03 · 1 source

Exhibit 4 preserves the two reported observations without converting them into CO2eS07

Exhibit 04

S07

Exhibit 04ExhibitsourcedGlobal fibre volume increased before any emissions calculation

Sourced observations from Textile Exchange Materials Market Report 2025 (S07): global fibre production across apparel, home textiles, footwear and other applications was 125 million tonnes in 2023 and 132 million tonnes in 2024. These are material volumes, not greenhouse gas emissions and not a Cameroon production baseline.

Read-outGlobal fibre volume increased before any emissions calculation

Method and source

Sourced observations from Textile Exchange Materials Market Report 2025 (S07): global fibre production across apparel, home textiles, footwear and other applications was 125 million tonnes in 2023 and 132 million tonnes in 2024. These are material volumes, not greenhouse gas emissions and not a Cameroon production baseline.

Unit: million tonnes of fibre per year. Status: sourced. Sources: S07.

The exhibit establishes a change in physical throughput, not a change in carbon. The corresponding carbon account would need to know which fibres entered which processes, under which energy and allocation assumptions.[S07][S23] That missing calculation is precisely the point: volume is an independent driver in the account and cannot be left outside the reduction narrative.

¶ 01 · 2 sources

S07S23

Product mix creates a related risk. If a factory shifts from lighter to heavier garments, emissions per piece may rise even when energy per kilogram falls. If it shifts towards products with longer verified service, emissions per wear may fall without the same movement per garment. The denominator must therefore remain attached to its decision, while the absolute total prevents a favourable ratio from concealing growth.[S08][S23]

¶ 02 · 2 sources

S08S23

Worked example

This illustrative case tests the relationship between volume, intensity and service. It does not represent a GFT factory, a measured garment or a forecast. The boundary is assumed to remain unchanged across both periods.

  1. Illustrative baseline: A manufacturer produces 100,000 accepted garments at 4.0 kg CO2e per garment. Absolute emissions are 100,000 * 4.0 = 400,000 kg CO2e, or 400 tonnes CO2e. These inputs are illustrative and chosen to make the arithmetic visible.[S08][S23]
  2. Illustrative following period: Output rises to 120,000 accepted garments while intensity improves to 3.5 kg CO2e per garment. Absolute emissions become 120,000 * 3.5 = 420,000 kg CO2e, or 420 tonnes CO2e. Intensity falls by 0.5 / 4.0 = 12.5 percent, but absolute emissions rise by 20,000 / 400,000 = 5.0 percent, all derived from the illustrative inputs.[S08]
  3. Illustrative service extension: If the baseline garments deliver 50 wears and the later garments deliver 70 wears under declared use scenarios, production emissions per wear are 4.0 / 50 = 0.080 kg CO2e and 3.5 / 70 = 0.050 kg CO2e. The per-wear result falls by 37.5 percent, derived from the illustrative assumptions, but the annual absolute total still rises by 5.0 percent.[S08][S23]
  4. Decision: The illustrative manufacturer has improved both product ratios and missed absolute reduction. The account should trigger a review of volume, energy, materials and sourcing rather than publish an unqualified reduction claim. Longer wear would support an absolute saving only if it actually displaced replacement production, which this arithmetic does not establish.[S08][S23]

This is why the paper refuses to choose between absolute and normalised measures. Total CO2e shows the burden that must fall. Carbon per accepted garment exposes process and product performance. Carbon per wear connects the account to service, provided wear counts and displacement assumptions are explicit.[S08][S23] Together they turn a reporting metric into a management constraint.

¶ 01 · 2 sources

S08S23

1.143 min · 9 paragraphs · read with a related exhibit

GFT's position is measure first, reduce second and claim last

Related · chapter 149 paragraphs step it

Related exhibit 64 · chapter 14Decision mapillustrativeThe first 90 days assign owners, evidence and decisions
Immediate governance chartersCore engineering and meter setupStandard administrative setupPhased supplier onboardingTechnical and systems setup effort →Criticality to baseline integrity →Accounting: chart and…Energy: sub-meters an…Production: yield and…Data: factor registry…Claims: sign-off and…Procurement: supplier…Review: dry-run audit…

Read-outAccounting: chart and boundary: Technical and systems setup effort 3, Criticality to baseline integrity 9.5. Quadrant: Immediate governance charters

Method and source

Illustrative 90-day pre-commissioning and start-up matrix derived from inventory governance and activity-data requirements in the GHG Protocol Corporate Standard (S04), UK DESNZ conversion factor activity rules (S20) and Scope 3 Technical Guidance (S23). Horizontal position scores setup effort across hardware and IT integration (0 to 10); vertical position scores criticality for locking a valid Phase 1 baseline (0 to 10). Coordinates are illustrative management-planning indices, not measured site performance.

Unit: illustrative readiness index (0 to 10). Status: illustrative. Sources: S04, S20, S23. Illustrative figures are teaching examples, not measured factory results.

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1.14 · Introduction · paragraph 1 of 9

The sequence begins with measurement because an unmanaged boundary can make any later statement ambiguous. It does not require perfect data before action. A factory can address an obvious energy loss while its wider Scope 3 screen is still developing. The rule is that the claimed effect must wait for a stable baseline, an activity record and a check that the burden has not moved elsewhere.[S01][S23]

Measurement also has a defined order of value. The first account should reveal decisions, not merely fill a disclosure template. It should show which garments, suppliers, processes and periods carry the largest emissions or uncertainties; which records are observed; and which assumptions could change the ranking.[S23] If the model cannot direct a meter request, a supplier conversation or an engineering test, it is not yet an operating tool.

Reduction comes second because the account should govern the intervention. Energy efficiency, material yield, process control, logistics and lower-carbon supply may all deserve attention, but their order depends on the actual hotspot and the feasibility of changing it.[S08][S23] Each action needs a baseline, an owner and a remeasurement plan. The review then separates three effects: a real change in activity, a change in production volume, and a change in emission factor or accounting method. Without that separation, a grid-factor update or a new proxy can be mistaken for an operational saving.

The absolute and intensity checks remain active during reduction. A successful line trial that lowers kWh per garment is useful evidence, but its scaled effect depends on runtime, output, product mix and any additional upstream burden. The product account tests whether the intervention lowers CO2e for the defined garment. The corporate account tests whether the organisation's relevant total falls over the comparable period.[S01][S04][S08] Reconciliation makes the two answers informative rather than contradictory.

Claims come last because their wording must inherit the account's limitations. A cradle-to-gate pilot can support a precisely named supplier-exchange result before it can support a full life cycle consumer claim. A scenario can disclose a possible use-phase outcome, but it cannot be described as measured consumer behaviour. A screening estimate can guide internal priorities without becoming a public product rating.[S01][S23]

Directive (EU) 2024/825 supplies a clear claims-control principle within its legal context: relevant product climate claims should be based on the actual life cycle impact of the product, not on offsetting outside its value chain.[S32] This chapter uses that Directive as an accounting and claims-design reference, not as legal advice on any market. The operational lesson is straightforward. An environmental initiative and a product footprint are separate accounts, and purchasing an offset does not repair an incomplete garment inventory.[S32]

This sequence gives the Cameroon textile programme a practical carbon workstream rather than a parallel reporting exercise. Feasibility analysis identifies the production system to be modelled. Performance management supplies the operating cadence and ownership. Digital strategy preserves versions, links and permissions. Carbon accounting joins those components by attaching a declared factor and boundary to physical activity, then carrying the result into product and corporate decisions. No measured footprint or saving is asserted before that evidence exists.

The discipline also sets a useful limit on ambition. GFT should not promise a universally lower-carbon Cameroon shirt, a complete environmental label or a neutral product. It should build the conditions under which a specific garment can be measured, compared on equivalent terms and improved without losing the absolute total. That is a narrower promise, but it is one that production evidence can support.

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16 sources · 121 citation marks on this pageMost cited: S23, 40 times

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R06 · Grade C · inherited record

Cameroon Trade Hub

Inherited evidence R06

About 95 percent of cotton fibre exported raw against 5 percent processed locally; industrialisation target of 50 percent local processing.

Publication date unrecorded. Inherited source-text record. The original publication has not been independently reopened for this web edition.

Chapter source notes

S01 GHG Protocol. 2011.

S23 GHG Protocol and Carbon Trust. 2013.

S05 International Organization for Standardization. 2018-08.

S11 Intergovernmental Panel on Climate Change. 2021-08-06.

S0101 World Resources Institute and World Business Council for Sustainable Development. 2011-09.

S31 Forfora et al., Sustainability. 2026-04-20.

S32 European Parliament and Council of the European Union. 2024-02-28.

S02 GHG Protocol. 2011.

S04 GHG Protocol. 2004.

S0102 World Resources Institute and World Business Council for Sustainable Development. 2004-03.

S08 Science Based Targets initiative and World Resources Institute. 2019.

S21 United Nations Industrial Development Organization. 2010.

R06 Cameroon Trade Hub. Publication date unrecorded; inherited source-text check.

S09 International Energy Agency. 2026.

S28 World Bank. 2025-01-16.

S07 Textile Exchange. 2025-09-18.

Keep the thread · chapter 01 of 14

Chapter 02 picks up the thread.

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02Part I: Build the account before the claim

Corporate and product accounts must reconcile without double counting

A controlled chart of accounts lets site emissions, supplier emissions and product emissions meet once and only once.

  • 2.1The organisational boundary determines direct responsibility
  • 2.4Scope 2 requires purchased energy evidence
  • 2.7The 15 Scope 3 categories become an apparel map
  • 2.9Cradle-to-gate and full life cycle factors have distinct uses
Reading time
36 min
Exhibits
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Sections
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