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Technical Manual · Carbon & Sustainability

Carbon Footprint Analyzer — Methodology & Formulas

Every input, equation, constant, output, and reference behind the Carbon Footprint Analyzer. All math covers GHG Protocol Scope 1/2/3 annual emissions and a full life-cycle assessment (EN 15978 stages A1–D), powered by the deterministic engine RZEngine.models.carbon anchored to locked data in DATA.carbon — no random values, no back-solved constants.

Engine RZEngine v2.5.x Basis GHG Protocol Corporate Standard LCA Basis ISO 14044 / EN 15978 Countries 32 Tabs 3 (Operational · LCA · Carbon Budget)
▶ Open the live Carbon Footprint Analyzer

01 Purpose & engineering basis

The Carbon Footprint Analyzer quantifies greenhouse-gas emissions from a data center across three boundary layers defined by the GHG Protocol Corporate Standard: direct emissions you own (Scope 1), electricity you purchase (Scope 2), and supply-chain and construction emissions you induce (Scope 3). It then extends those annual figures across the full cradle-to-grave facility lifetime via a life-cycle assessment aligned to EN 15978 (Sustainability of construction works, calculation method for environmental performance of buildings, stages A1–D).

A third tab allocates the resulting annual emissions against the host country's nationally-determined contribution (NDC) under the Paris Agreement, mapping the facility's share of the national carbon budget across sectors (AI training, inference, cloud, enterprise, government) and computing the gap to net-zero by the user's target year. This is a screening-grade planning model, not a certified corporate carbon disclosure.

02 Inputs

Inputs span three operational groups (power, location, Scope 1 sources, renewables) plus a lifecycle group for the LCA tab and a budget-allocation group for the Carbon Budget tab.

Tab 1 — Operational

Field / IDSymbolUnitRange / defaultMeaning
IT Load itLoadPITkW50–100 000 · default 1 000Rack-level IT power draw (servers + storage + network). Does not include cooling or power-distribution overhead.
PUE pueValuePUEratio1.1–2.5 · default 1.58Total facility power ÷ IT power. Multiplies IT load to give facility power. Industry average 1.58 (Uptime 2026).
Country countrySelectISO-2 enum32 countriesSelects grid emission factor and electricity rate from COUNTRIES[] (patched at runtime from RZEngine.data.countries).
Grid intensity gridIntensityEFgridkgCO₂e/kWhread-only · auto-filledNational average emission factor for purchased electricity. Source: IEA 2026 + Ember. Range 0.02 (SE) to 0.90 (ZA).
Generator fuel genTypeenumdiesel / hvoStandard diesel 2.68 kgCO₂/L; HVO (hydrotreated vegetable oil) 0.54 kgCO₂/L (~80% lower).
Generator test hours genHoursHgenh/yr50–500 · default 200Annual hours of generator operation including monthly testing, load-bank tests, and unplanned outages.
Cooling type coolingTypeenumair_crac / inrow / rdhx / dlcSelects refrigerant GWP and charge rate. R-410A (GWP 2088), R-134a (GWP 1430), R-1234ze (GWP 7).
Annual leak rate leakRateLr%1–15 · default 5Fraction of total refrigerant charge that escapes annually. Industry average 5–10% for DX; 2–3% for chilled-water plants.
Renewable strategy renewableTypeenumnone / solar / solar_bess / ppaProcurement mechanism. Determines co-investment note only; the emission reduction is applied via renewablePct.
Renewable coverage renewablePctR%0–100 · default 0Percentage of facility electricity matched by renewable energy or certificates. Applied to derive market-based Scope 2.

Tab 2 — Life-Cycle Assessment

Field / IDUnitDefaultMeaning
Facility size facilityMWMW ITlinked to itLoadTotal IT capacity; scales material quantities, floor area, and server counts per MW.
Building type buildingTypeenumpurposeMultiplier on material quantities: purpose-built = 1.0, converted warehouse = 0.70, modular = 0.85.
Concrete grade concreteGradeenumc30C30 = 150 kgCO₂e/t; C40 = 250 kgCO₂e/t; low-carbon GGBS blend = 100 kgCO₂e/t. ICE Database v4.1.
Steel sourcing steelSourceenumworld_avgWorld-average (30% recycled) = 1850 kgCO₂e/t; EAF (90%+) = 500 kgCO₂e/t; BOF virgin = 2200 kgCO₂e/t.
Seismic zone seismicZone0–40Structural mass multiplier: Zone 0 = 1.0×, Zone 1 = 1.05×, Zone 2 = 1.12×, Zone 3 = 1.25×, Zone 4 = 1.40×.
Workload type workloadTypeenumtraditionalSets server embodied carbon (kgCO₂e) and density (servers/MW): traditional 1200/1250, cloud 1200/1000, H100 4000/140, B200 3500/200.
Server refresh cycle serverRefreshyr4Replacement period; drives number of IT refresh cycles over project lifetime.
Network refresh networkRefreshyr5Network-switch replacement cycle.
Project lifetime projectLifetimeyr20Total facility operational life for LCA amortisation and lifetime operational total.
Battery chemistry batteryTypeenumvrlaUPS battery: VRLA = 68 kgCO₂e/kWh (5yr life); LFP = 62 kgCO₂e/kWh (10yr); NMC = 74 kgCO₂e/kWh (8yr).
Battery runtime batteryRuntimemin10UPS hold-time at full IT load; sets total battery kWh = facilityMW × 1000 × (runtime/60) × redundancyMult.
Redundancy redundancyLCAenumn1N = 1.0×, N+1 = 1.25×, 2N = 2.0×, 2N+1 = 2.25× on battery and MEP quantities.
Equipment origin equipOriginenumregionalTransport multiplier on A4+A5: local (<500 km) = 0.8×, regional = 1.0×, international = 1.5×.
Construction duration constructDurationmonths18Scales A4+A5 construction-activity carbon linearly vs the 18-month reference basis.
Decommission plan decommPlanenumdemolitionEnd-of-life multiplier on C1–C4: demolition = 1.0×, refurbishment = 0.5×, deconstruction/reuse = 0.2×.
Steel recycle % steelRecycle%92Module-D recycling credit on structural steel (92% industry average).
Copper recycle % copperRecycle%85Module-D recycling credit on copper cabling and busbars.

03 Calculation methodology

All emission calculations follow GHG Protocol Corporate Standard (2015 edition) for Scope 1/2/3 boundaries, and EN 15978:2011 / ISO 14044:2006 for LCA stages. Function names map one-to-one to RZEngine.models.carbon in rz-engine.js.

Scope 2 — Purchased grid electricity

facilityKWh = PIT × PUE × 8 760 h/yr effectiveEF = EFgrid × (1 − R / 100) [market-based] Scope 2 = (facilityKWh / 1 000) × effectiveEF [tCO₂e/yr] In RZEngine.models.carbon.annualTonnes(mw, pue, region). Market-based method: renewable coverage R% directly reduces the effective emission factor. Location-based = R set to 0. GHG Protocol · IEA 2026

Scope 1a — Generator diesel / HVO combustion

fuelConsumed = PIT [kW] × 0.3 L/kW·h × Hgen [h/yr] [L/yr] genEmissions = fuelConsumed × EFfuel / 1 000 [tCO₂e/yr] EFfuel: diesel 2.68 kgCO₂/L (EPA 2024); HVO 0.54 kgCO₂/L (~80% life-cycle reduction). Diesel consumption rate 0.3 L/kW·h is the engine constant DIESEL_CONSUMPTION_RATE. EPA Emission Factors 2024 · GHG Protocol

Scope 1b — Fugitive refrigerant leakage

totalCharge = PIT [kW] × chargeKgPerKw [kg refrigerant] refrigEmissions = totalCharge × (Lr / 100) × GWP / 1 000 [tCO₂e/yr] chargeKgPerKw and GWP are per-cooling-type constants: air_crac 0.30 kg/kW / GWP 2088; inrow 0.20 / 2088; rdhx 0.15 / 1430; dlc 0.05 / 7. GWP₁₀₀ values: IPCC AR4 (sitewide-consistent). GHG Protocol · IPCC AR4 · EPA GreenChill

Scope 3 simplified (operational tab)

Scope 3ops = PIT [kW] × 0.15 tCO₂e/kW [tCO₂e/yr upstream] A screening upstream-supply-chain factor used on the operational tab only (0.15 tCO₂e/kW IT = ~15 kgCO₂e per MWh IT). The LCA tab provides a full cradle-to-gate Scope 3 breakdown with material-level emission factors. GHG Protocol Scope 3 Standard · RICS/LETI

LCA — Stage A1–A3: Material production (embodied carbon)

concreteCarbon = facilityMW × 1 000 t/MW × EFconcrete × buildMult × seismicMult / 1 000 steelCarbon = facilityMW × 200 t/MW × EFsteel × buildMult × seismicMult / 1 000 copperCarbon = facilityMW × 20 t/MW × 4 100 kgCO₂e/t / 1 000 aluminumCarbon = facilityMW × 10 t/MW × 10 000 kgCO₂e/t / 1 000 pvcCarbon = facilityMW × 7 t/MW × 2 800 kgCO₂e/t / 1 000 materialsTotal = concreteCarbon + steelCarbon + copperCarbon + aluminumCarbon + pvcCarbon [tCO₂e] All results in tCO₂e. EFconcrete: C30 150, C40 250, low-carbon 100 kgCO₂e/t. EFsteel: world-avg 1850, EAF 500, BOF 2200 kgCO₂e/t. Quantities per MW IT: concrete 1 000 t, steel 200 t, copper 20 t, aluminium 10 t, PVC 7 t — from RICS/LETI DC embodied-carbon studies. buildMult: purpose 1.0, converted 0.7, modular 0.85. seismicMult: zone 0–4 = [1.0, 1.05, 1.12, 1.25, 1.40]. ICE Database v4.1 · RICS/LETI · EN 15978

LCA — IT equipment embodied carbon (Scope 3 upstream)

totalServers = facilityMW × serversPerMW serverCycles = ceil(projectLife / serverRefresh) networkCycles = ceil(projectLife / networkRefresh) itEmbodied = ( totalServers × EFserver × serverCycles + totalServers × 0.05 × 450 kgCO₂e × networkCycles + totalServers × 0.02 × 2 000 kgCO₂e × serverCycles ) / 1 000 [tCO₂e] EFserver per workload: traditional 1 200 kgCO₂e (1 250 servers/MW), cloud 1 200 (1 000/MW), H100 GPU 4 000 (140/MW), B200+ GPU 3 500 (200/MW). Network switches at 5% of server count × 450 kgCO₂e; storage arrays at 2% × 2 000 kgCO₂e. Dell/HPE/NVIDIA published LCA · GHG Protocol Scope 3

LCA — UPS battery embodied carbon

batteryKWh = facilityMW × 1 000 × (batteryRuntime / 60) × redundancyMult batteryCarbon = batteryKWh × EFbattery / 1 000 [tCO₂e/cycle] batteryReplacements = ceil(projectLife / battChemLife) totalBatteryCarbon = batteryCarbon × batteryReplacements [tCO₂e] EFbattery: VRLA 68 kgCO₂e/kWh (5yr life); LFP 62 (10yr); NMC 74 (8yr). redundancyMult: N=1.0, N+1=1.25, 2N=2.0, 2N+1=2.25. PEFCR Battery (2020) · IVL Swedish Environment Institute

LCA — MEP equipment, construction activity, end-of-life (A4–C4)

mepCarbon = facilityMW × 150 tCO₂e/MW (UPS + cooling + gensets + switchgear) floorArea = facilityMW × 500 m²/MW constructCarbon = floorArea × 40 kgCO₂e/m² × transportMult × (duration / 18) / 1 000 endOfLifeCarbon = floorArea × 15 kgCO₂e/m² × decommMult / 1 000 transportMult: local 0.80, regional 1.00, international 1.50. decommMult: demolition 1.0, refurbishment 0.5, deconstruction 0.2. Construction activity factor 40 kgCO₂e/m² covers plant diesel, formwork, site waste (A5). RICS Embodied Carbon Primer 2020 · EN 15978

LCA — Module D: End-of-life recycling credits

steelCredit = facilityMW × 200 t × (steelRecycle% / 100) × 1 500 kgCO₂e/t / 1 000 copperCredit = facilityMW × 20 t × (copperRecycle% / 100) × 3 000 kgCO₂e/t / 1 000 alCredit = facilityMW × 10 t × 0.85 × 9 000 kgCO₂e/t / 1 000 moduleDCredit = −(steelCredit + copperCredit + alCredit) [tCO₂e, negative] Recycling credit = avoided primary production. Factors: steel 1 500, copper 3 000, aluminium 9 000 kgCO₂e/t saved. Aluminium recycled fraction fixed at 85% (industry average). Module D is reported separately and does not reduce the A1–C4 total. ICE Database v4.1 · EN 15978 Module D

Carbon budget allocation (Tab 3)

dcSectorEmissions = nationalTotal × (dcShare% / 100) [MtCO₂e/yr] targetDcEmissions = dcSectorEmissions × (1 − ndcReduction) cumulativeBudget = (dcSectorEmissions + targetDcEmissions) / 2 × budgetYears [linear] annualBudgetPerMW = cumulativeBudget / budgetYears / nationalMW × 1 000 [tCO₂/MW/yr] NDC reduction = |ndcTarget%| / 100. nationalMW estimated as dcSectorEmissions / (0.475 kgCO₂/kWh × 8.76 × 1.58). Three budget methodologies: linear trajectory, front-loaded (×0.85), back-loaded (×1.15). UNFCCC NDC Registry · Paris Agreement Art. 4

Carbon offset and compliance cost

offsetCost = totalEmissions [tCO₂e] × $35 /tCO₂e [voluntary market] taxExposure = totalEmissions × $65 /tCO₂e [EU ETS 2025 proxy] In RZEngine.models.carbon.offsetCost(tonnes) and the inline EU ETS exposure. DATA.carbon.offsetPrice = $35 (voluntary market 2026 blend; reconciles DCMOC $45 vs legacy $18). EU ETS proxy $65 = ~€60/tCO₂ (2025 forward). Singapore NCCS S$45/t from 2026 also surfaced. World Bank Carbon Pricing Dashboard · OECD ECR 2025 · DATA.sources['carbon']

04 Constants & data sources

All grid factors and carbon prices are locked in DATA.carbon with provenance tags in DATA.sources['carbon']. Material emission factors live in the inline LCA constant in carbon-footprint.html, crossreferencing ICE Database v4.1 and RICS/LETI studies.

Grid emission factors (kgCO₂e/kWh) — DATA.carbon.gridFactor

RegionEF (kgCO₂e/kWh)Notes
US0.37US EIA national average (coal+gas+nuclear+renewables mix)
EU0.23EU27 average (high nuclear FR/SE, coal-heavy PL pulled)
APAC0.55Blended Asia-Pacific (China/India dominate)
LATAM0.20High hydro share (BR, CO, CL)
ID (Indonesia)0.68Coal-heavy PLN grid; per-country COUNTRIES[] = 0.70
SG (Singapore)0.41CCGT gas-dominant grid; per-country = 0.40
JP (Japan)0.47Post-Fukushima gas/coal, nuclear restart partial
IN (India)0.63Coal-heavy; per-country = 0.72
MY (Malaysia)0.55Gas+coal Peninsular; per-country = 0.60
FR (France)0.06~70% nuclear (per-country table)
SE (Sweden)0.02Hydro + wind dominant
ZA (South Africa)0.90Coal-dominant Eskom grid

Source: DATA.sources['carbon'] = 'IEA 2026 + Ember grid intensity + ICAP carbon prices', asOf 2026.

At runtime, carbon-footprint.html patches per-country values from RZEngine.data.countries[id].environment.gridCarbonIntensity (the single source of truth generated from dcmoc/src/constants/countries.ts). The 32-country per-country table shown in the tool supersedes the 9-region DATA.carbon.gridFactor blends for the calculator.

Carbon prices ($/tCO₂e) — DATA.carbon.carbonPrice

RegionPrice ($/tCO₂e)Regime
US40Blended state-level compliance + RGGI + voluntary
EU85EU ETS 2025 (compliance, ~€80/t converted)
APAC25Blended SEA/APAC compliance schemes
LATAM15Colombia/Chile voluntary + compliance blend
ID12Indonesia ETS pilot + voluntary market
SG18NCCS S$25/t 2024 (S$45/t from 2026)
JP30Japan GX-ETS + J-Credit scheme
IN10India PAT + voluntary carbon market
MY14Bursa Carbon Exchange + voluntary blend

Source: DATA.sources['envCosts'] = 'World Bank Carbon Pricing Dashboard + OECD ECR 2025 + NCCS Singapore', asOf 2026-07.

Material emission factors — LCA constant

MaterialkgCO₂e/tQuantity/MW ITSource
Concrete C301501 000 tICE Database v4.1, RICS/LETI DC
Concrete C402501 000 tICE Database v4.1
Concrete low-carbon (GGBS 50%)1001 000 tRICS/LETI
Steel — world average (30% recycled)1 850200 tICE Database v4.1
Steel — EAF (90%+ recycled)500200 tICE Database v4.1
Steel — BOF virgin2 200200 tICE Database v4.1
Copper (primary)4 10020 tICE Database v4.1
Aluminium (primary)10 00010 tICE Database v4.1
PVC cable2 8007 tICE Database / Ecoinvent 3.9

Engine model — DATA.carbon anchors

ConstantValueUnitNotes
DATA.carbon.embodiedPerMw3 200tCO₂e/MWBulk embodied carbon for engine's models.carbon.embodiedTonnes(mw). Covers concrete+steel+MEP screening estimate. RICS/LETI DC studies.
DATA.carbon.dieselKgCo2PerL2.68kgCO₂/LEPA Emission Factors 2024.
DATA.carbon.genTestHoursPerYear52h/yrEngine default (1 h/week monthly test). Calculator uses user-provided 50–500 h.
DATA.carbon.refrigerantLeakTco2ePerMwYr8tCO₂e/MW·yrEngine Scope 1 screening; GHG Protocol + EPA GreenChill typical ranges.
DATA.carbon.offsetPrice35$/tCO₂eVoluntary market 2026 blend (nature-based + engineered); reconciles DCMOC $45 vs legacy $18. DATA.sources['carbon.offsetPrice'].

05 Outputs

OutputFormula / sourceUnitInterpretation
Annual total emissionsscope1 + scope2 + scope3tCO₂e/yrGHG Protocol total boundary. Primary KPI on the operational tab.
Scope 1genEmissions + refrigEmissionstCO₂e/yrDirect on-site emissions: generator fuel combustion + fugitive refrigerant leaks.
Scope 2 (market-based)annualMWh × effectiveEFtCO₂e/yrPurchased electricity adjusted for renewable certificates/PPAs.
Scope 3 (simplified)PIT × 0.15tCO₂e/yrUpstream IT supply chain screening factor (operational tab only).
Carbon intensitytotalEmissions × 1000 / (PIT × 8760)kgCO₂e/kWh ITEfficiency grade: A+ <0.1, A <0.2, B <0.4, C <0.6, D <0.8, E <1.0, F ≥1.0.
Offset costtotalEmissions × $35$/yrVoluntary market neutralisation cost at 2026 blend price.
Tax exposuretotalEmissions × $65$/yrIndicative EU ETS-proxy compliance cost (not the applicable rate outside EU).
LCA embodied (A1–A3)materialsTotaltCO₂eOne-time cradle-to-gate: concrete + steel + copper + aluminium + PVC.
IT embodied (Scope 3)itEmbodiedtCO₂eLifetime server+network+storage manufacturing emissions across all refresh cycles.
Battery carbon (total)batteryCarbon × batteryReplacementstCO₂eUPS battery manufacturing over project life (all replacement cycles).
Module D credit−(steelCredit + copperCredit + alCredit)tCO₂eEnd-of-life recycling benefit — negative value, reported separately from A1–C4 total per EN 15978.
Lifetime operationaltotalEmissions × projectLifetCO₂eCumulative operational footprint over the facility lifetime.
Lifetime total (LCA + ops)totalLCA + lifetimeOperationaltCO₂eCradle-to-grave total: all construction, IT, and operational emissions over project life.
Annual budget per MWNDC derivation (see § 03)tCO₂/MW/yrNational DC-sector carbon budget allocated per MW of installed capacity.

06 Worked example

Default inputs: 1 000 kW IT, PUE 1.58, United States (grid 0.40 kgCO₂e/kWh), diesel generator 200 h/yr, air_crac cooling (R-410A, GWP 2088, 0.30 kg/kW, 5% leak), no renewables, 1 MW facility, purpose-built, concrete C30, steel world-average, traditional workload, VRLA battery 10 min N+1, 20-year life. All numbers verified by node -e against the engine logic.

  1. Facility energy: 1000 kW × 1.58 PUE × 8760 h = 13 840.8 MWh/yr
  2. Scope 2: 13 840.8 MWh × 0.40 kgCO₂/kWh = 5 536 tCO₂e/yr
  3. Scope 1a — generator diesel: 1000 kW × 0.30 L/kW·h × 200 h × 2.68 kgCO₂/L / 1000 = 160.8 tCO₂e/yr
  4. Scope 1b — refrigerant: total charge 1000 × 0.30 = 300 kg; leak 300 × 0.05 × 2088 / 1000 = 31.3 tCO₂e/yr; Scope 1 total 192 tCO₂e/yr
  5. Scope 3 (simplified): 1000 kW × 0.15 = 150 tCO₂e/yr
  6. Annual total: 192 + 5536 + 150 = 5 878 tCO₂e/yr → Carbon intensity 5878 × 1000 / (1000 × 8760) = 0.671 kgCO₂e/kWh IT → Grade D (below average)
  7. Offset cost: 5878 × $35 = $205 730/yr
  8. LCA A1–A3 materials (1 MW, C30, world-avg steel): concrete 1000 t × 150 = 150 t, steel 200 t × 1850 = 370 t, copper 20 t × 4100 = 82 t, aluminium 10 t × 10 000 = 100 t, PVC 7 t × 2800 = 20 t → 722 tCO₂e embodied (A1–A3)
  9. IT embodied (traditional, 20yr / 4yr refresh = 5 cycles): 1 250 servers × 1 200 kgCO₂e × 5 cycles + 62.5 switches × 450 × 4 cycles + 25 storage × 2 000 × 5 cycles = 7 863 tCO₂e over life
  10. Battery carbon (VRLA, 10 min, N+1, 5yr replace → 4 cycles): 1000 kW × (10/60) min × 1.25 × 68 kgCO₂e/kWh / 1000 × 4 cycles = 56.7 tCO₂e
  11. MEP + construction + EOL: 150 + 20.0 + 7.5 = 177.5 tCO₂e
  12. Module D recycling credits (steel 92%, copper 85%, Al 85%): steel 200 × 0.92 × 1500 = 276 t, copper 20 × 0.85 × 3000 = 51 t, Al 10 × 0.85 × 9000 = 76.5 t → −404 tCO₂e (benefit)
  13. Total LCA (excl. ops): 722 + 7863 + 56.7 + 177.5 − 404 = 8 415 tCO₂e
  14. Lifetime operational (20yr): 5878 × 20 = 117 560 tCO₂e
  15. Cradle-to-grave total: 8415 + 117 560 = 125 975 tCO₂e over 20 years
Reading: for this typical 1 MW colo in the US, Scope 2 electricity dominates at ~94% of annual emissions. Switching to 100% renewable PPA reduces Scope 2 to near zero, cutting the annual total to ~342 tCO₂e and flipping the grade from D to A+. On a lifetime basis, IT equipment manufacturing (7 863 t) exceeds the entire building structure (722 t) by ~11×, reflecting the embodied-carbon intensity of AI/GPU hardware. Low-carbon steel (EAF) would reduce the steel line from 370 t to 100 t — a 73% saving on structural steel alone.

07 References & standards

08 Assumptions & limitations

Scope boundaries: Scope 2 is calculated on the market-based method only (location-based = renewable coverage set to 0%). Scope 3 upstream on the operational tab is a screening factor (0.15 tCO₂e/kW IT); the LCA tab provides a more granular Scope 3 upstream via per-material emission factors and IT-equipment LCAs, but does not include purchased goods and services beyond IT hardware, business travel, waste, or water.

Grid factors: National average emission factors from IEA/Ember do not represent the marginal emission rate of an additional data-center load on any specific grid or hour. Time-of-use or hourly matching (24/7 CFE methodology) is not modelled. For high-renewable grids (France, Sweden), the national average already reflects near-zero grid intensity.

Material quantities per MW: Concrete 1 000 t/MW, steel 200 t/MW, copper 20 t/MW, aluminium 10 t/MW, PVC 7 t/MW are industry planning estimates from RICS/LETI DC embodied-carbon studies. They are screening-grade benchmarks; actual quantities depend on structural design, site conditions, and equipment specification.

IT embodied carbon: Server-embodied values (1 200–4 000 kgCO₂e/unit) are from published manufacturer LCA declarations or peer-reviewed studies. AI GPU server values (H100 4 000, B200 3 500 kgCO₂e) are estimates based on the Dell/NVIDIA hardware and will improve as manufacturers publish more detailed LCA reports.

Regulatory compliance: Carbon tax exposure is computed using the EU ETS proxy ($65/tCO₂e) as an indicative figure only. Actual compliance obligations depend on the jurisdiction, emission category, facility classification, and applicable scheme thresholds. SEC Climate Disclosure, EU CBAM, and Singapore NCCS exposures cited in the tool are informational only and do not constitute legal or compliance advice.

Carbon budget allocation: The NDC-derived per-MW budget is a macro screening estimate derived from national total emission budgets and a static DC-sector share percentage. It does not account for electricity generation emissions already included in Scope 2, temporal emission pathways within each country's sector, or sub-national policy variations.

This calculator is an engineering education and pre-design planning aid. Carbon footprints for corporate GHG reporting under GHG Protocol, ISO 14064, SEC Rule, or EU taxonomy must be prepared or validated by a qualified sustainability professional with access to site-specific metered data and certified grid factors.

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