Wireless Charger

Electronics
Medium Confidence

Carbon Cost Index Score

52 kgCO₂e / per unit

Per kg

208 kgCO₂e / kg

Methodology v1.0 · Last reviewed 2026-04-08

Scope Breakdown

Scope kgCO₂e % of Total Distribution
Scope 1 4.16 8%
Scope 2 7.8 15%
Scope 3 40.04 77%
Total 52 100%

Emission Hotspots

Emission Hotspot Scope Est. % of Total
use-phase electricity consumption S3 48%
battery/circuit board production S1 28%
raw material extraction (metals, plastics) S1 18%
distribution and transportation S3 4%
end-of-life and disposal S3 2%

Manufacturing Geography

Region
China
Grid Intensity
555 gCO2/kWh (IEA 2023)

Material Composition Assumptions

This assessment assumes a typical wireless charger weighing approximately 250 grams with the following material breakdown:

The material composition emphasizes electromagnetic components required for wireless power transfer, with substantial plastic housing to protect internal electronics and provide user safety.

Manufacturing Geography

Primary manufacturing occurs in China, which produces the majority of consumer electronics globally due to established supply chains and specialized component availability. The Chinese electricity grid operates at an average carbon intensity of 555 gCO2/kWh, reflecting the country’s mixed energy portfolio with significant coal dependence alongside growing renewable capacity. This manufacturing location choice stems from proximity to semiconductor fabs, metal processing facilities, and plastic component suppliers, enabling cost-effective integration of diverse material inputs required for wireless charging technology.

Regional Variation

Manufacturing RegionGrid IntensityEstimated CCI ScoreAdjustment vs Default
China555 gCO2/kWh52Baseline
South Korea436 gCO2/kWh48-8%
Germany311 gCO2/kWh43-17%
Costa Rica89 gCO2/kWh35-33%
Norway17 gCO2/kWh32-38%

Provenance Override Guidance

Suppliers can submit the following data types to override the default CCI score with product-specific information:

  1. Manufacturing facility electricity source documentation showing renewable energy procurement contracts or on-site generation capacity
  2. Bill of materials with specific recycled content percentages for plastic housing, copper coils, and aluminum components
  3. Transportation logistics data including shipping distances, modes, and fuel efficiency for primary distribution routes
  4. Component supplier environmental product declarations for printed circuit boards, semiconductors, and magnetic materials
  5. End-of-life material recovery rates and recycling partnerships demonstrating improved disposal outcomes

Methodology Notes

Related Concepts

Sources

  1. Bi et al. 2015 Applied Energy — Found that electricity consumption during device operation represents the primary environmental impact driver for electronic charging systems.
  2. Heo & Bae 2017 LCA Mobile Phone Charger — Demonstrated that raw material extraction phases contribute significantly more carbon emissions than manufacturing processes for charging devices.
  3. Fairphone 2022 Life Cycle Assessment — Showed that incorporating recycled materials into electronic device production can meaningfully reduce overall carbon footprints.
  4. Ericsson 2013 Life Cycle Assessment Smartphone — Established baseline methodologies for evaluating environmental impacts across mobile device accessory lifecycles.
  5. Yang et al. 2019 Power Bank LCA — Identified battery component manufacturing as a critical hotspot for portable charging device environmental impacts.
  6. Cordella 2021 Journal of Industrial Ecology — Quantified regional variations in electronic device carbon footprints based on local electricity grid carbon intensities.
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