
iLearnNGrow Princess Hair Accessories Set (Pink)
Description says “Designed with kids in mind, this hair accessories set is made from safe, durable, and gentle materials that hold hair securely without tugging or discomfort.”
per item, whole life · sold in India · made in India
- Raw materials 0.14 kg · 6.4%
- Production 1.63 kg · 75%
- Packaging 0.15 kg · 6.9%
- Distribution 0.054 kg · 2.5%
- End of life 0.20 kg · 9.3%
Change anything below and the footprint recalculates. What you change is marked “Stated”. Nothing here is saved.
| Part | Material (kg CO₂e per kg) | Share % | Mass | Source |
|---|---|---|---|---|
| Material | Family word, assumption applied ⓘ | 300 g | Estimated Primary source |
In everyday terms, about the same as driving 13 km in a petrol car, 272 smartphone charges, or 0.1 tree-years of absorption.
How this was calculated
Everything behind the figure, for auditors and the curious. Built to the requirements of ISO 14040/44, ISO 14067 and PACT v3.
Standards checkISO 14040/44, ISO 14067 and PACT v3, requirement by requirement
All 30 requirements, with clauses
| Requirement | ISO 14040/44 | ISO 14067 | PACT v3 |
|---|---|---|---|
| The study's purpose is written down | Met §4.2.2 | Met §6.3.1 | — |
| No public claim that one product beats another | Met §4.2.2, 4.2.3.7 | Met §Annex A, Annex B | — |
| The unit is clear, and a partial footprint is labelled as such | Met §4.2.3.2 | Met §6.3.3 | Met §3.2.4 |
| The system boundary is described | Met §4.2.3.3 | Met §6.3.4, 7.3 b | Met §3.2.3 |
| The time period is stated and justified | — | Met §6.3.6 | Met §3.2.3 |
| Product category rules are used where they exist | — | Met §6.2 | Met §3.1.2 |
| Anything left out is small, estimated and reported | Met §4.2.3.3.3 | Met §6.3.4.3 | Met §3.3.1.2 |
| The data is checked for consistency | Met §4.3.2–4.3.3 | Met §6.4.3 | — |
| Own processes use measured data, or say why not | — | Met §6.3.5 | Met §4.1.3 |
| Every database value is referenced and fit for purpose | Met §4.3.2 | Met §6.3.5 | Met §4.1.3.2 |
| Shared factory burdens are split by the standard rules | Not applicable §4.3.4 | Not applicable §6.4.6 | Not applicable §3.3.1.4 |
| Recycling is counted with the cut-off method | Met §4.3.4.3 | Met §6.4.6.3 | Met §3.3.2.2 |
| Electricity covers its whole life cycle | Met §4.3.2–4.3.3 | Met §6.4.9.4.1 | Met §3.3.2.3 |
| Electricity follows the market-based rules | — | Met §6.4.9.4.4 | Met §3.3.2.3, Box 7 |
| Land-use change is counted and shown separately factor does not state whether dLUC is covered for pk1. Fix: Use a factor with a separate dLUC result, or supply material.land_use_change with its value, source, year and whether the material factor already includes it. A documented no-LUC statement can resolve an unknown coverage gap. | — | Not met §6.4.9.5 | Not met §3.3.2.4 |
| Biogenic carbon is counted in and out | — | Met §6.4.9.2, 6.4.9.3, 6.5.2 | Met §3.3.2.4 |
| Air freight is shown separately, without radiative forcing | — | Not applicable §6.4.9.7 | Not applicable §3.3.2.1 |
| No offsets or avoided emissions | — | Met §6.3.4.1 | Met §3.3.2.2 |
| Latest IPCC warming factors (AR6, 100 years) 94.9 % of cradle-to-gate emissions use AR5 factors; PACT allows only the latest IPCC report once its grace year has passed. Fix: Replace these factors with AR6-characterised data. | Justified §4.4.2 | Justified §6.5.1 | Not met §3.2.2 |
| Fossil and biogenic methane are kept apart | — | Met §6.5.2 | — |
| Key choices are stress-tested | Met §4.5.3.3 | Met §6.4.5, 6.6 | — |
| Uncertainty is assessed | — | Met §6.6 | — |
| Data quality is scored | Met §4.2.3.6 | Met §6.3.5 | Met §4.2.2, 4.2.3 |
| Limitations are stated | Met §4.5.4 | Met §6.6, Annex A | — |
| Results are broken down the required way | — | Met §7.2 | Met §3.3.1, data model |
| The study report contains every required item | Met §5.2 | Met §7.3 | — |
| The PACT data file is complete Missing or invalid: companyIds, productIds. Fix: Add company and product identifiers (URNs such as urn:mfp:company:acme), the reference period and a PACT unit. | — | — | Not met §6.1; Tech Specs v3.0.3 |
| The primary data share is reported | — | — | Met §4.2.2 |
| Independent critical review No critical review recorded. Fix: Commission an ISO 14071 critical review before any public communication; a panel review is mandatory for public comparisons. | Needs reviewer §6 | Needs reviewer §8 | — |
| Third-party verification of the calculation model The MFP footprint calculation model has not yet been verified by a third party. Fix: Commission limited-assurance verification of the calculation model (PACT v3 §5.3.3, Tables 14–15). | — | — | Needs reviewer §5.3.3 |
These standards apply to studies. This checklist reports the implemented checks; it is not certification or a substitute for independent review. “Needs reviewer” items (critical review, verification of the calculation model) can only be closed by an independent third party.
Assumptions and defaults21 entries, 2 warnings
- Grid electricity uses location-based national or regional averages. PACT v3 and Catena-X require the market-based residual mix where contractual instruments exist; supply electricity_factor for contracted or residual-mix power.
- Temporal scores for desnz_2025 use the edition year; their underlying data are older, so those temporal scores may be better than the data deserve.
Assumptions register · 21 entries
- Screening mode: this listing gives no primary data, so every input below that is not a stated material or weight is a named screening default. The result is not PACT-conformant (primary data share 0 %).
- Product mass 0.3 kg is a category typical value for "accessory", not a measured weight.
- Country of manufacture not stated in the listing; India assumed.
- m1: material matched from "without" (family, MEDIUM confidence): wood named in another language, modelled as tropical sawn hardwood.
- m1: material share 100 % is estimated from the listing text.
- Packaging not stated; screening default for accessory: Paper bag / wrap 50 g paper, recycled, Shipping box (share) 80 g corrugated board.
- Landfill of wood and bamboo is modelled with the library's paper landfill factor, the closest available; no wood landfill factor is on file.
- Cutting, stitching & finishing: Bag / small leather goods assembly energy: 2 kWh per item (Default assumption (cut, stitch, finish)).
- Process energy is unmetered screening data (activity uncertainty GSD 1.5–2.0), on the IN grid.
- Inbound transport of materials to the factory is left out of the total, because supplier locations are unknown; its likely size is estimated and reported under the cut-off rule below.
- Distribution route is a screening default (1,000 km road), carrying product plus packaging.
- Cut-off rule: processes are excluded only where no verified data exists, and each exclusion is estimated where possible and reported (ISO 14044 §4.2.3.3.3). Inbound transport is estimated at 0.0188 kg CO₂e.
- raw_materials.m1: dLUC 0.0006782 kgCO2e/kg added from globaltimber23_tropical_hardwood, whose source reports it separately from the factor value.
- Wood carbon: IPCC 2006 Vol.5 Table 2.4 defaults for wood products (85 % dry matter, 50 % C of dry, no fossil carbon); carbon in panel adhesives is not separated.
- Paper/board carbon: IPCC 2006 Vol.5 Table 2.4 defaults (90 % dry matter, 46 % C of dry, 1 % fossil).
- Secondary (library) factors are scored at least 3 on technology: PACT v3 Table 12 reserves scores 1-2 for primary data.
- Use-phase scenario: No energy-using use phase for accessory.
- End-of-life route shares: MFP screening scenario for India, not PEFCR: textiles and leather goods 80 % landfill / dump, 5 % burning; plastics 60 % / 10 %; paper 40 % / 5 %; metals and glass 50 % landfill; the rest recovered (cut-off). Anchored on CPCB Annual Report on Solid Waste Management 2021-22 (24 % landfilled, 22 % unaccounted).
- Incineration: 100 % oxidation of carbon assumed (IPCC 2006 Vol.5 Ch.5 default oxidation factor for MSW incineration). Energy-recovery credits are not applied under cut-off.
- Aggregated secondary factors are used as published in their own GWP basis (AR5); only gas-split fuel factors and direct gas emissions are characterised with AR6. Residual inconsistency is typically a few percent for CO2-dominated factors.
- Sources quoted as published figures (not open-licensed datasets): epdhub_globaltimber_2023, fba_lca_2020. Replace with licensed or supplier data before external or comparative claims.
SensitivityThe figure with other published choices
The footprint recalculated with each alternative choice: other published factors, the other allocation method, the grid mix instead of a green-power contract, and the use profile at its uncertainty bounds. A large change shows where better data pays off first.
| Line | Choice tested | Baseline | Alternative | Δ kg CO₂e | Δ % |
|---|---|---|---|---|---|
| Wood | Emission factor | Tropical sawn hardwood, kiln-dried, GWP-fossil | Wood, generic blend (UK DESNZ material use, primary) DESNZ (2026) Government greenhouse gas conversion factors for company reporting, flat file (revised July 2026), row ID 19_500_5048_15_1; Methodology paper 2026 section 12 and Appendix 1 | -0.059 | -2.7% |
| Wood | Emission factor | Tropical sawn hardwood, kiln-dried, GWP-fossil | Hardwood, kiln-dried rough-sawn (Australia) Forest and Wood Products Australia (2015) Environmental Product Declaration: Hardwood Timber, EPD Registration No. S-P-00561, Version 1, Australasian EPD Programme, Table 2 | +0.028 | +1.3% |
| Shipping box (share) | Emission factor | Corrugated product, U.S. industry average (56 % recovered fibre) | Board, primary UK DESNZ GHG conversion factors 2025, Material use | -0.001 | 0% |
Every line of the calculation17 lines: activity × factor, with sources
Footprint = Σ activity × emission factor
Every line: how much (activity) × how much CO₂e per unit (factor), with its source. Source labels
| Stage | Line | Activity | × Factor | = kg CO₂e | DQR | Source |
|---|---|---|---|---|---|---|
| Raw materials | Wood wood_hardwood (virgin) | 0.300 kg | 0.4655 kg/kg | 0.140 | 3/5/4 Low · +288% | Primary source EPD Hub HUB-0367, 'Dried tropical sawn timber sourced from certified forests in Congo basin', Global Timber A/S (DK), EN 15804+A2 & ISO 14025, One Click LCA, 2023 database · 2023 |
| Raw materials | Wood land-use change published with the factor direct land-use change | 0.300 kg | 0.0006782 kg/kg | 0.000 | 3/5/4 Low · +288% | Primary source EPD Hub HUB-0367, 'Dried tropical sawn timber sourced from certified forests in Congo basin', Global Timber A/S (DK), EN 15804+A2 & ISO 14025, One Click LCA, 2023 computed |
| Packaging | Paper bag / wrap paper (100% recycled, cut-off) | 0.050 kg | 1.05 kg/kg | 0.053 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Material use database · 2025 (flat file) |
| Packaging | Shipping box (share) corrugated_board (industry average, 56 % recovered fibre) | 0.080 kg | 1.21 kg/kg | 0.097 | 3/5/5 Very low · +307% | Primary source NCASI and Anthesis for the Corrugated Packaging Alliance (AF&PA, FBA, AICC, TAPPI), '2020 Life Cycle Assessment of U.S. Average Corrugated Product', final report v2 (cradle-to-gate results added), 6 Nov 2023; ISO 14040/14044, critical review by Athena Sustainable Materials Institute database · 6 Nov 2023 (2020 data) |
| Production | Cutting, stitching & finishing grid electricity IN | 2.000 kWh | 0.8135 kg/kWh | 1.627 | 3/1/1 High · +554% | Pin to primary Ember via Our World in Data, carbon intensity of electricity database · 2026 release (2025 data) |
| Distribution | Road to customer (India) HGV (all diesel), all HGVs, average laden, 1000 km | 0.430 t·km | 0.1252 kg/t·km | 0.054 | 3/5/1 Medium · +309% | Pin to primary UK DESNZ GHG conversion factors 2025, Freighting goods + WTT delivery vehicles database · 2025 (flat file) |
| End of life | Wood to recycling (cut-off: collection only) | 0.165 kg | 0.004686 kg/kg | 0.001 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal (open/closed loop, combustion) database · 2025 (flat file) |
| End of life | Wood to incineration: collection | 0.015 kg | 0.004686 kg/kg | 0.000 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal (open/closed loop, combustion) database · 2025 (flat file) |
| End of life | Wood to landfill biogenic non-CO₂ (landfill methane) | 0.120 kg | 1.164 kg/kg | 0.140 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal database · 2025 (flat file) |
| End of life | Paper bag / wrap to recycling (cut-off: collection only) | 0.027 kg | 0.004686 kg/kg | 0.000 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal (open/closed loop, combustion) database · 2025 (flat file) |
| End of life | Paper bag / wrap to incineration: collection | 0.003 kg | 0.004686 kg/kg | 0.000 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal (open/closed loop, combustion) database · 2025 (flat file) |
| End of life | Paper bag / wrap incineration fossil CO2 (stoichiometric, full oxidation) | 0.003 kg | 0.01517 kg/kg | 0.000 | 1/1/1 High · +0% | Computed Carbon mass balance (this engine) computed |
| End of life | Paper bag / wrap to landfill biogenic non-CO₂ (landfill methane) | 0.020 kg | 1.164 kg/kg | 0.023 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal database · 2025 (flat file) |
| End of life | Shipping box (share) to recycling (cut-off: collection only) | 0.044 kg | 0.004686 kg/kg | 0.000 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal (open/closed loop, combustion) database · 2025 (flat file) |
| End of life | Shipping box (share) to incineration: collection | 0.004 kg | 0.004686 kg/kg | 0.000 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal (open/closed loop, combustion) database · 2025 (flat file) |
| End of life | Shipping box (share) incineration fossil CO2 (stoichiometric, full oxidation) | 0.004 kg | 0.01517 kg/kg | 0.000 | 1/1/1 High · +0% | Computed Carbon mass balance (this engine) computed |
| End of life | Shipping box (share) to landfill biogenic non-CO₂ (landfill methane) | 0.032 kg | 1.164 kg/kg | 0.037 | 3/5/1 Medium · +271% | Pin to primary UK DESNZ GHG conversion factors 2025, Waste disposal database · 2025 (flat file) |
| Total, excluding biogenic uptake | 2.172 |
ISO 14067 study reportSeparately reported values and report contents
ISO 14067 study report · Carbon footprint (cradle-to-grave, functional unit)
| Footprint per one accessory delivered and used to the end of its life, sold in India (ISO 14067, incl. biogenic −1/+1) | 1.5424 kg CO₂e |
| Net fossil GHG | 1.9712 kg CO₂e |
| Biogenic CO₂ emissions | 0.0331 kg CO₂ |
| Biogenic CO₂ removals | -0.6624 kg CO₂ |
| Biogenic CH₄ (as CO₂e) | 0.2003 kg CO₂e |
| Direct land-use change | 0.0002 kg CO₂e |
| Aircraft (no radiative forcing) | 0.0000 kg CO₂e |
| Biogenic carbon content | 0.1275 kg C |
| Outbound logistics (reported separately) | 0.0538 kg CO₂e |
| Raw materials | 0.1399 kg · 6.44% |
| Production | 1.6270 kg · 74.92% |
| Inbound transport | 0.0000 kg · 0% |
| Packaging | 0.1493 kg · 6.88% |
| Distribution | 0.0538 kg · 2.48% |
| Use phase | 0.0000 kg · 0% |
| End of life | 0.2016 kg · 9.28% |
| Goal: application, reasons, audience, comparative assertion §6.3.1 / 14044 4.2.2 | Screening carbon footprint shown on the Made for Planet catalogue so brands and buyers can see where a product's emissions come from. Reasons: No company data is available for this listing; a transparent estimate from the listing and published factors shows the likely size and the main stages. Audience: Brands and buyers (business-to-business). The estimate is also displayed on madeforplanet.com, labelled as a screening estimate; it is not an environmental claim the brand may use in marketing. Public comparative assertion: no. |
| Functional or declared unit and reference flow §7.3 a | Functional unit: one accessory delivered and used to the end of its life, sold in India; reference flow 0.3 kg of product. |
| System boundary §7.3 b | cradle to grave. Screening: materials, processing energy, packaging, distribution, use and end of life. Capital goods are excluded, as is usual for attributional product footprints. Stages modelled: raw_materials, packaging, production, distribution, end_of_life. |
| Significant unit processes §7.3 c | wood_hardwood (virgin) (6.43 %); assembly: grid electricity IN (74.92 %); m1 to landfill (6.43 %) |
| Data sources §7.3 d | Global Timber tropical sawn hardwood EPD (HUB-0367) 2023; 2020 Life Cycle Assessment of U.S. Average Corrugated Product (final report v2, cradle-to-gate results added) 6 Nov 2023 (2020 data); UK DESNZ Greenhouse gas reporting: conversion factors 2025 2025 (flat file); Carbon intensity of electricity (Ember via Our World in Data) 2026 release (2025 data) |
| Greenhouse gases considered §7.3 e | CO₂, CH₄ (fossil and biogenic), N₂O and refrigerant gases (HFCs, SF₆, NF₃) where present; secondary factors cover the gases their publishers include. |
| Characterisation factors §7.3 f | IPCC AR6 GWP100 with climate-carbon feedbacks; secondary factors in their published basis where no AR6 version exists (see gwp check). |
| Cut-off criteria and exclusions §7.3 g, o | Inbound transport of materials to the factory: 0.018783 kg CO₂e (screening estimate: 0.300 kg of materials × 500 km by average lorry (UK DESNZ GHG conversion factors 2025, Freighting goods + WTT delivery vehicles); supplier locations are not known) |
| Allocation procedures §7.3 h | No multi-output processes. Recycling: cut-off. |
| Timing of emissions §7.3 i, 6.4.8 | All emissions and removals counted as at the start of the assessment period; no delayed-emission weighting. |
| Data description and quality §7.3 j | PACT Table 12 DQR: technological 3, geographical 2, temporal 1.37; per-line scores, confidence and 95 % uncertainty in the inventory. |
| Sensitivity and uncertainty §7.3 k | 3 sensitivity case(s); lognormal Monte Carlo on pedigree uncertainty. |
| Electricity treatment §7.3 l | IN: grid location (India electricity, life-cycle intensity 2025) |
| Interpretation, limitations §7.3 m, Annex A | Climate change only: other impacts (water, land, toxicity, biodiversity) are not assessed, so a lower footprint does not mean a lower environmental impact overall. Secondary factors limit accuracy as shown by the data-quality scores. |
| Value choices §7.3 n | Cut-off for recycling (PACT); economic allocation only above a 5× value ratio; conservative factor where published values disagree (see sensitivity). |
| Scope changes and exclusions §7.3 o | None. |
| Life-cycle stages, use and end-of-life scenarios §7.3 p, 6.3.7, 6.3.8 | Use-phase scenario: No energy-using use phase for accessory. End-of-life route shares: MFP screening scenario for India, not PEFCR: textiles and leather goods 80 % landfill / dump, 5 % burning; plastics 60 % / 10 %; paper 40 % / 5 %; metals and glass 50 % landfill; the rest recovered (cut-off). Anchored on CPCB Annual Report on Solid Waste Management 2021-22 (24 % landfilled, 22 % unaccounted). |
| Influence of alternative scenarios §7.3 q | factor_choice m1: -2.7 %; factor_choice m1: 1.3 %; factor_choice pk2: 0 % |
| Period the footprint represents §7.3 r, 6.3.6 | 2026-01-01 to 2026-12-31: current production as represented by the factor library (each factor's own data year is scored in the temporal data quality) |
| Product category rules §7.3 s, 6.2 | No product category rules conforming to ISO/TS 14027 are known for this product category; MFP screening rules are applied and disclosed. |
| Performance tracking §7.3 t, 6.4.7 | Not a performance-tracking study. |
ISO 14067 counts biogenic removals (−1) and emissions (+1) in the carbon footprint; the PACT headline excludes biogenic uptake. Both are shown.
PACT v3 data and biogenic carbonData-exchange values and a downloadable file
PACT v3 data model (cradle-to-gate) and biogenic carbon balance
Download PACT v3.0.3 JSON ProductFootprint in the Technical Specifications v3.0.3 format (decimals as strings). Check the conformance panel before sending it.
| Footprint excl. biogenic uptake | 1.9162 kg CO₂e |
| Footprint incl. biogenic uptake | 1.2538 kg CO₂e |
| Fossil GHG emissions | 1.9160 kg CO₂e |
| Land-use change GHG | 0.0002 kg CO₂e |
| Biogenic non-CO₂ | 0.0000 kg CO₂e |
| Biogenic CO₂ uptake | -0.6624 kg CO₂ |
| Fossil carbon content | 0.0000 kg C |
| Biogenic carbon content | 0.1275 kg C |
| Aircraft GHG (no RF) | 0.0000 kg CO₂e |
| Packaging GHG | 0.1493 kg CO₂e |
| Exempted emissions | 0.9710 % |
| Primary data share | 0.0000 % |
| IPCC characterisation | AR6, AR5 |
| Biogenic CO₂ uptake | -0.6624 kg CO₂ |
| Biogenic CO₂ emitted | 0.0331 kg CO₂ |
| Biogenic C stored in landfill | 0.0723 kg C |
| Biogenic C exported to recycling | 0.0994 kg C |
| Biogenic C in product | 0.1275 kg C |
| Engine / factor library | 1.2.0 / 2026.11-mfp.8 |