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How does deforestation for data centres affect forests and local environments?

No study measures forest clearing from data centre construction itself, but roads and mines show that infrastructure can drive forest loss far beyond the land it clears.

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Covers: This page covers the direct and indirect environmental effects of clearing forest for data centre construction, including habitat loss, carbon emissions, soil and water impacts, and local climate effects. It does not cover broader debates about data centre energy use or water consumption unless directly tied to land clearing.

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Aerial view of a clearing in a dense forest
Photo: Benjamin Hibbert-Hingston

The short answer

Evidence-backed AI-prepared starting map

No study in the available evidence measures forest clearing caused specifically by data centre construction. The closest measured analogues are other land-hungry infrastructure: a global analysis of roads finds forest loss extending up to 5 km from infrastructure with a clear distance-decay effect, totalling 4.26 million km², or 10.7% of 2020 global forest extent, with the tropics accounting for 54.8% of severe, worsening degradation. Mining removed 16,268 km² of forest cover worldwide from 2001 to 2022, 65.64% of it in tropical and subtropical regions, with about half tied to gold, coal, bauxite, nickel-cobalt and copper. In sub-Saharan Africa, mining caused 187,000 hectares of direct deforestation and triggered an additional 8.0 percentage points of deforestation within 1 km of a mine, with effects persisting up to 20 km for at least ten years.123

What this rests on4 independent sources
  • Evidence 14
  • Interpretation 3

In brief

  1. No available study measures forest clearing specifically for data centre construction; the measured evidence comes from roads and mining.12

    Interpretation
  2. Road-linked forest loss extends up to 5 km from infrastructure and totals 4.26 million km², or 10.7% of 2020 global forest extent, with the tropics bearing the worst and worsening degradation.1

    Evidence-backed
  3. Mining removed 16,268 km² of forest cover from 2001 to 2022, 65.64% in tropical and subtropical regions, with about half from five commodities including copper and nickel-cobalt.2

    Evidence-backed
  4. Offsite loss can dwarf direct clearing: in sub-Saharan Africa each hectare of direct mining deforestation triggered on average 34 hectares of additional loss within five years, and effects persisted up to 20 km for at least ten years.3

    Evidence-backed
  5. Forest outcomes around infrastructure depend on governance and local human activity, not just on the amount of land physically cleared.13

    Evidence-backed

At a glance

The picture in numbers

Live · updated just now

Global analysis of roads

10.7%

11 in every 100

of 2020 global forest extent lost to road-linked forest loss1
Global mining mapping, 2001–2022

16,268 km²

16,268 km²: Forest cover removed by mining worldwide2
Global mining mapping, 2001–2022

65.6%

66 in every 100

of mining deforestation in tropical and subtropical regions2

The evidence behind it

4 sources
  • Other studies and data4

Published in 2026

Sources on this page by kind and year
SourceKindYear
Flexibility-aware framework for efficient planner-initiated siting of data center.Other studies and data2026
Global impacts of transportation infrastructure on forest degradation and lossOther studies and data2026
Mapping global resource driven nature loss in the mining sector from 2001 to 2022.Other studies and data2026
Mining triggers extensive additional deforestation in sub-Saharan Africa.Other studies and data2026

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What it means for you

Which fits you?

Pick the situation closest to yours. Each answer says what it rests on.

If you are assessing a proposed data centre site near forest

treat the cleared footprint as a lower bound: road and mining evidence shows fragmentation and induced activity spread loss kilometres beyond the direct clearing, so ask for assessment of a buffer zone rather than the site boundary alone.13

Interpretation

If you are reviewing an environmental impact assessment for a project that clears forest

the sub-Saharan Africa mining study argues for embedding offsite deforestation levels into impact assessments, since offsite loss averaged 34 hectares per hectare of direct loss within five years.3

Evidence-backed

If you are weighing where a large data centre load should connect

flexible operation expanded the modelled siting frontier by 9–17% at 1 GW and 19–21% at 2 GW on a synthetic Texas system, which widens the set of candidate locations and therefore the choice of whether forest is cleared at all.4

Evidence-backed

If you are relying on protected-area status to prevent forest loss near new infrastructure

global protected areas were found to have insufficient capacity to curb ongoing road-linked degradation, so designation alone should not be treated as a safeguard.1

Evidence-backed

If you are sourcing minerals for data centre hardware such as copper, cobalt or nickel

these commodities were among the largest contributors to mining-driven deforestation, and cobalt and copper mines caused the highest additional offsite deforestation in sub-Saharan Africa.23

Evidence-backed

If you are comparing forest impacts across regions

the tropics carried 54.8% of severe, worsening road-linked degradation and 65.64% of mining deforestation, while the Global North showed milder impacts with partial recovery.12

Evidence-backed

The full story · 2 chapters

01

What the evidence shows about forest loss from land-hungry infrastructure

AI summary:Roads and mining show forest loss spreading well beyond cleared footprints, shaped by local activity and governance.

Evidence-backed

Evidence-backed: Roads are the best-studied linear infrastructure threat to forests. Impacts extend up to 5 km from the infrastructure with a clear distance-decay effect, and the global total reaches 4.26 million km² of forest loss, equivalent to 10.7% of the 2020 global forest extent. Road-adjacent forests lose cover, height and productivity and become more fragmented. The Global South, with the tropics accounting for 54.8%, faces severe and worsening degradation over 2000–2020, while the Global North shows milder impacts with partial recovery. The authors find that road-linked degradation is tightly coupled with local human activity, that global protected areas have insufficient capacity to curb ongoing degradation, and that differences among regions are tied to governance choices.1

Evidence-backed

Evidence-backed: Mining shows how a single industrial land use can drive both direct and offsite forest loss. From 2001 to 2022, mining removed 16,268 km² of forest cover worldwide, with 65.64% in tropical and subtropical regions. Roughly half of that deforestation came from extracting gold, coal, aluminium (bauxite), nickel-cobalt and copper, primarily in countries intersecting the Amazon, Southeast Asian and Congo Basin rainforests. Deforestation-to-mining-area ratios and biodiversity risks vary by location, and conservation threats do not always scale with deforestation rates.2

Evidence-backed

Evidence-backed: In sub-Saharan Africa, mining caused 187,000 hectares of direct deforestation from pits, tailing ponds and spoil heaps, and triggered an additional 8.0 percentage points (95% CI: 7.2–8.9 pp) of deforestation within 1 km of a mine compared with unmined areas. Elevated deforestation of 1.1 pp (95% CI: 0.7–1.5) persisted up to 20 km from mines even after ten years. For every hectare of direct deforestation from the mine footprint, mining triggered on average 34 hectares of additional offsite loss within five years through ancillary activities including agriculture and settlements. Mines extracting cobalt and copper, key energy transition minerals, caused the highest additional deforestation.3

Interpretation

Interpretation: The pattern across both road and mining evidence is that direct clearing is only part of the story: fragmentation, edge effects and induced activity spread loss well beyond the cleared footprint, and the spread is shaped by local human activity and governance rather than by the infrastructure type alone.13

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02

What is known about data centre siting decisions

AI summary:A modelling study shows how flexibility and pre-certified envelopes shift where and how fast large data centre loads can connect.

Evidence-backed

Evidence-backed: One modelling study addresses where large data centre loads can connect to the grid. Applied to a synthetic 2000-bus Texas power system, it finds that operational flexibility expands the siting frontier by 9–17% at 1 GW and 19–21% at 2 GW compared with firm operation, with median all-hour average prices essentially unchanged at $24.32/MWh for the 2 GW cases and peak-hour price dispersion attenuated by about 3.4%. Using pre-certified envelopes to bypass major transmission reinforcements enables first energization in 12–18 months, a conservative reduction of 3.5–4 years versus the conventional 5–8 year project-led process. This bears on land clearing only indirectly: it describes how siting options and timelines shift, not what happens to forests at the chosen site.4

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Sources

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  1. 1
    Global impacts of transportation infrastructure on forest degradation and loss
    Nature Communications (Zhou et al.)Published Feb 4, 2026Checked Oct 6, 2026
    “Impacts extend up to 5 km with a clear distance decay effect, totaling 4.26 million km2 of forest loss—equivalent to 10.7% of the 2020 global forest extent. The Global South (tropics accounting for 54.8%) faces severe, worsening degradation (2000–2020), while the Global North shows milder impacts, with partial recovery. Critically, 89% of grid cells exhibit conflicting long-term trends across metrics, highlighting the inadequacy of cover-only assessments. We further find that road-linked degradation is tightly coupled with local human activity, and that global protected areas have insufficient capacity to curb ongoing degradation. Differences in impacts among regions suggest that road-linked forest degradation is tied to governance choices—urging integrated transport-forest planning to balance development and conservation. Transportation infrastructure threatens forests, but past studies have been regional or focused on single metrics like forest cover. This global analysis finds road-adjacent forests lose cover, height, and productivity and become more fragmented.”
  2. 2
    Mapping global resource driven nature loss in the mining sector from 2001 to 2022.
    Nature communications (Cheng et al.)Published May 28, 2026Checked Oct 6, 2026
    “Here, we introduce a novel approach integrating remote sensing, machine learning, and cloud computing to classify approximately 70,000 mining sites by commodity. Using this newly detailed dataset, we quantify the nature loss associated with 20 extracted commodities, focusing on deforestation and habitat destruction. From 2001 to 2022, mining activities worldwide resulted in the removal of 16,268 km² of forest cover, with 65.64% occurring in tropical and subtropical regions. Notably, approximately half of this deforestation was attributed to the extraction of gold, coal, aluminium (bauxite), nickel-cobalt and copper, primarily in countries intersecting the Amazon, Southeast Asian, and Congo Basin rainforests. Our analysis also reveals that deforestation-to-mining area ratios and biodiversity risks vary by mining location, and conservation threats do not always scale with deforestation rates. By providing commodity-specific maps of mining-induced nature loss, our work equips companies and organisations with actionable insights to identify risks within their supply chains and implement targeted mitigation strategies.”
  3. 3
    Mining triggers extensive additional deforestation in sub-Saharan Africa.
    Nature (Morton et al.)Published Jun 3, 2026Checked Oct 6, 2026
    “In total, we find 187,000 hectares of direct mining-driven deforestation, that is, deforestation due to features directly associated with mining operations, such as pits, tailing ponds and spoil heaps. We estimate that mining also triggers an additional 8.0 percentage points (pp; 95% confidence interval (CI): 7.2-8.9 pp) increase in deforestation within 1 km of a mine compared with unmined areas. Increased levels of deforestation (1.1 pp, 95% CI: 0.7-1.5) persist up to 20 km from mines even after ten years. For every hectare of direct deforestation due to the mine footprint, mining triggers, on average, 34 hectares of additional offsite loss within five years through ancillary activities, including agriculture and settlements. Mines extracting cobalt and copper-key energy transition minerals-caused the highest amount of additional deforestation. Embedding offsite deforestation levels into environmental impact assessments for new mining projects will be key to ensuring zero-deforestation or no-net-loss supply chains for critical minerals and reduce future mining-driven forest losses in sub-Saharan Africa.”
  4. 4
    Flexibility-aware framework for efficient planner-initiated siting of data center.
    Nature communications (Kim et al.)Published May 16, 2026Checked Oct 6, 2026
    “Applied to a synthetic 2000-bus Texas power system, the framework demonstrates that operational flexibility expands the siting frontier by 9-17% at 1 GW and 19-21% at 2 GW compared to firm operation. Median all-hour average prices remain essentially unchanged ($24.32/MWh for the 2 GW cases), and the shift envelope attenuates peak-hour price dispersion by approximately 3.4% with minimal side effects during off-peak hours. Utilizing pre-certified envelopes to bypass major transmission reinforcements, this workflow enables first energization in 12-18 months-a conservative reduction of 3.5-4 years versus the conventional 5-8 year project-led process. This technology-agnostic framework provides a proactive decision-making tool for system operators and regulators to fast-track large flexible loads while preserving grid reliability and market stability.”

How it changed

Published 1 time since Oct 6, 2026.

  1. Version 2Oct 6, 2026Live now

    AI-prepared Starting Map from live research.

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  • “What is known about data centre siting decisions” rests on one independent source

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Open questions

  • How much forest is cleared directly for data centre campuses, access roads and power infrastructure, and how does that footprint compare with roads or mines of similar investment size?

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  • Do data centres trigger offsite forest loss the way mines do, through worker settlement, new roads and induced agriculture, and over what distance and time frame?

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  • How much of the forest impact depends on siting decisions, such as choosing previously cleared land or brownfield grid connections instead of forested sites?

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  • Do protected areas and permitting rules curb forest loss around data centre sites, given evidence that protected areas have insufficient capacity to curb road-linked degradation?

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