The Carbon Footprint of Office Furniture
Carbon Case for Reuse, Refurbishment and Recycling in the Office Furniture Sector
Introduction
Office furniture—including desks, chairs, sofas, and storage units—embodies significant carbon emissions. These embodied carbon emissions occur during raw material extraction, manufacturing, assembly, and transportation. Once furniture is produced, these emissions are essentially locked in.
This report consolidates data from public sector agencies, academic life cycle assessments (LCAs), and industry benchmarks to present:
- Typical embodied carbon of new office furniture
- Emissions savings from reuse and refurbishment
- Emissions avoided through material recycling
- Strategic guidance for procurement, policy, and practice
Emissions Snapshot: New vs Refurbished Furniture
| Furniture Item | Carbon if Bought New (kg CO₂e) | Carbon if Refurbished (kg CO₂e) | Carbon Saved (kg CO₂e) | % Carbon Reduction | Key Refurbishment Actions |
|---|---|---|---|---|---|
| Swivel Chair | 72 | 10 | 62 | 86% | Reupholstered, partial parts replaced, cleaned |
| Meeting Chair | 38 | 7 | 31 | 82% | Reupholstered, cleaned |
| Armchair | 55 | 8 | 47 | 85% | Deep cleaned only |
| 2 Seater Sofa | 90 | 10 | 80 | 89% | Deep cleaned only |
| 3 Seater Sofa | 110 | 10 | 100 | 91% | Deep cleaned only |
| Rectangular Workstation | 65 | 20 | 45 | 69% | Resized, powder coated metal, cleaned |
| Meeting Table | 60 | 10 | 50 | 83% | Deep cleaned only |
| Radial Workstation | 75 | 22 | 53 | 71% | Resized, powder coated metal, cleaned |
| Wooden Pedestal | 44 | 10 | 34 | 77% | Deep cleaned only |
| Wooden Bookcase | 45 | 10 | 35 | 78% | Deep cleaned only |
| Wooden Cupboard | 60 | 12 | 48 | 80% | Deep cleaned only |
| Wooden Filing Cabinet | 58 | 12 | 46 | 79% | Deep cleaned only |
| Metal Pedestal | 50 | 12 | 38 | 76% | Cleaned (90%), powder coated (10%) |
| Metal Tambour Unit | 52 | 13 | 39 | 75% | Cleaned (90%), powder coated (10%) |
| Metal Cupboard | 55 | 14 | 41 | 75% | Cleaned (90%), powder coated (10%) |
| Metal Filing Cabinet | 54 | 14 | 40 | 74% | Cleaned (90%), powder coated (10%) |
| Screen Divider | 55 | 10 | 45 | 82% | Reupholstered (90%), cleaned (10%) |
Emissions from Recycling (by Material)
| Material Type | Route | CO₂e Saving (kg/kg) | Notes |
|---|---|---|---|
| Steel, aluminium (metals) | Recycling | 8.18 | Avoids virgin production |
| Wood (MDF, plywood, MFC) | Biomass (energy) | 4.97 | Displaces fossil fuel energy |
| Plastic (PP, nylon) | Recycling | 4.97 | Avoids virgin polymer production |
| Foam / Fabric / Leather | RDF (energy) | 1.00 | Used in waste-to-energy incineration |
| Mixed/unknown materials | RDF (energy) | 1.00 | Conservative default value |
Methodology
To ensure credibility, this report relies on a transparent calculation framework using publicly available data. We applied cradle-to-gate emissions accounting and included conservative assumptions to prevent overestimating savings.
Weight assumptions (per item):
- Swivel Chair: ~10–14 kg (mostly metal and plastic)
- Desk: ~25–35 kg (primarily chipboard/MFC with steel frame)
- Storage (cupboards, filing cabinets): ~20–35 kg (wooden or steel variants)
Average refurbishment emissions are calculated using known energy and material use:
- Reupholstery: Includes fabric production, adhesive use, and workshop energy (~2.5 kg CO₂e)
- Powder coating: High-temperature curing process for metal frames (~6 kg CO₂e)
- Component replacement: Assumes steel or plastic gas lifts, castors, or arms (~4 kg CO₂e per swap)
- Cleaning: Energy and water use in industrial cleaning (~1 kg CO₂e)
Savings are the difference between the original new item's cradle-to-gate footprint and the cumulative impact of refurbishment actions. Where multiple refurbishment processes are applied to an item, these emissions are aggregated based on probability/frequency of occurrence (e.g. 90% reupholstery).
1. Carbon for New Furniture
- Sourced from FIRA (2011), WRAP, and published manufacturer LCAs
- Values are cradle-to-gate estimates (excludes use phase)
2. Carbon for Refurbishment
- Based on actual refurbishment activities and weighted by their frequency of use
- Estimated emissions: Reupholstery: 2–3 kg, Powder coating: 5–8 kg, Component swap: 3–5 kg, Cleaning: ~1 kg
3. Carbon for Recycling
- Based on UK and EU waste carbon metrics
- Sources include Zero Waste Scotland, DEFRA, and WRAP conversion factors
- Applied using typical furniture mass and material compositions
Sources
- FIRA (2011) – Benchmarking Furniture Carbon Footprints
- WRAP (2011) – Benefits of Reuse: Office Furniture
- Zero Waste Scotland (2022) – Carbon Metric Reports
- University of British Columbia (2023) – Reuse vs New LCA Study
- DEFRA/BEIS (2023) – GHG Conversion Factors
Strategic Recommendations
The office furniture industry has a key role to play in the circular economy. These recommendations apply across sectors—from public procurement to interior designers and facilities managers.
- Prioritise Refurbishment First: Educate procurement teams on the significant carbon reductions from reuse. Encourage tendering that includes refurbished options.
- Only Recycle When Reuse Isn’t Viable: Ensure waste streams are sorted at dismantling facilities to maximise recycling outcomes, particularly for metal and wood.
- Require Circular Procurement: Integrate remanufacturing standards (FIRA REMAN001) into contracts, especially in government, education, and large corporations.
- Fund Refurbishment Services: Provide grants or tax credits to SMEs and social enterprises remanufacturing furniture, especially outside major cities.
- Track and Disclose Carbon Savings: Develop an industry-wide standard for measuring and disclosing CO₂e savings tied to furniture reuse.
- Educate Designers and Buyers: Promote reuse as an aesthetic and functional option. Provide CPDs and design guides for architects and fit-out specialists.
- Prioritise Refurbishment First: Reuse saves 70–90% of carbon emissions compared to new.
- Only Recycle When Reuse Isn’t Viable: Particularly valuable for clean metals and plastics.
- Require Circular Procurement: Adopt remanufacturing standards (e.g. FIRA REMAN001).
- Fund Refurbishment Services: Support regional reuse hubs and logistics.
- Track and Disclose Carbon Savings: Integrate furniture into carbon reporting frameworks.
- Educate Designers and Buyers: Promote understanding of furniture lifecycle impacts.
Carbon Savings Certificates and Client Reporting
To help organisations realise the impact of their sustainable procurement and disposal choices, we issue a Carbon Savings Certificate for every project involving reuse, refurbishment, or recycling.
Each certificate includes:
- Total carbon saved (kg CO₂e)
- Breakdown by product and material type
- Methodology overview referencing this report
- Tangible impact equivalents (e.g. miles not driven)
Equivalency metric: For ease of understanding, we compare emissions savings to avoided driving emissions:
- 1 kg CO₂e saved = 4 miles not driven
- This is based on a UK fleet-average vehicle emission of 0.28 kg CO₂e/mile (source: DEFRA GHG Conversion Factors, 2023)
This approach supports sustainability reporting and corporate carbon reduction targets, and helps embed circular economy practices in real-world decision-making.
Transparency and Credibility
All values were compiled in 2025 using a rigorous process designed to ensure transparency, repeatability, and public traceability. No commercial consultancy data or proprietary emissions claims were included.
Data Quality Controls:
- Where multiple sources existed for similar products, the most conservative estimate was selected to avoid over-claiming.
- Cross-validation: Furniture weights and refurbishment emissions were triangulated across 3 or more public datasets.
- Recycling factors were taken directly from UK government-endorsed publications and peer-reviewed sources.
Discrepancy Management:
- If literature varied significantly, median values were used.
- Where manufacturer-specific data existed but was not replicable (e.g. promotional claims), it was excluded.
This approach supports alignment with PAS 2050 and GHG Protocol Product Standard practices.
All values were compiled in 2025 from:
- UK government sources (WRAP, DEFRA, BEIS)
- Peer-reviewed academic LCAs
- Open-source manufacturer disclosures (excluding proprietary or branded consultant data)
Calculations use conservative assumptions, verified references, and cradle-to-gate methodology. This report avoids commercial consultant estimates and instead relies on public evidence for decision-making.
This guide is intended as a centralised reference for the office furniture and interiors industry to improve transparency, carbon literacy, and low-impact procurement strategies.

