The Economics & Ecology of Landscape Restoration

We provide quantitative models, land acquisition frameworks, and hard ecological data for large-scale rewilding projects. No abstract theories. Real figures for real habitats.

Latest Figures (2024)

  • Peatland Carbon Yield 4.5t CO₂e / ha / yr
  • UK Grade 3 Arable £8,500 - £10,000 / acre
  • BNG Unit Price (Est.) £25,000 - £35,000

Data updated quarterly based on primary market research and DEFRA disclosures.

Conservation is an Allocation Problem.

The transition from marginal agriculture to restored wildland is hindered by a lack of rigorous financial modelling. Environmental NGOs speak in moral imperatives; landowners speak in yield per hectare.

Bridging this gap requires treating ecological restoration as a capital-intensive infrastructure project. This means calculating precise natural capital ROI, understanding baseline soil degradation, and structuring complex mixed-revenue streams (carbon, biodiversity net gain, eco-tourism).

Key Research Areas

Carbon Yield Modeling

Estimating carbon sequestration requires baseline habitat data. Our models do not rely on global averages; they use specific soil types, rainfall data, and intervention methods to project realistic yields.

  • Baseline: Degraded upland pasture (mineral soils).
  • Intervention: Mixed native broadleaf woodland creation.
  • Timeline: 30-50 year verifiable increments.
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Yield Projection (Broadleaf)

Year Cumulative (tCO₂e/ha) Annual Rate
Year 5 12.4 2.48
Year 15 85.6 7.32
Year 30 245.0 10.60
Year 50 410.2 8.26

*Indicative data based on Woodland Carbon Code metrics for Sycamore/Ash/Birch mixtures on optimal soils.

The Land Acquisition Playbook

Buying land for nature recovery requires a different approach to traditional agricultural or commercial property acquisition.

1. Identifying Marginality

The highest ecological ROI comes from acquiring Grade 4 or 5 agricultural land that is economically unviable without heavy subsidy. We map topographical data against historical crop yields to identify prime targets.

Read the guide →

2. Soil Baseline Testing

Never acquire without a rigorous soil carbon and nutrient baseline. Over-fertilised soils (high phosphorus) will require years of nutrient stripping before species-rich grassland can establish.

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3. Title & Sporting Rights

Severed mineral or sporting rights can fatally undermine a rewilding project. If a third party holds the right to shoot deer, natural grazing densities cannot be controlled.

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4. Community Integration

Landscape-scale changes provoke local resistance. Structuring acquisition via community buyouts, or establishing immediate local economic ties (e.g., contracting local graziers) is critical for political viability.

Read the guide →

Our Positions

Isn't rewilding just abandoning land? +
No. In a heavily modified landscape without apex predators or megafauna, passive abandonment usually results in homogenous scrub or invasive species dominance. Effective rewilding requires intensive initial intervention: drain blocking, fence removal, seed inoculation, and the introduction of proxy herbivores (e.g., Exmoor ponies, Tamworth pigs) managed in complex rotational patterns.
Does this threaten food security? +
We advocate for restoring marginal, unproductive land. In the UK, for example, the least productive 20% of agricultural land produces only 3% of the calories. Shifting this land to ecological recovery while intensifying production on high-grade soils via precision agriculture is a mathematically sound strategy for maintaining caloric output while reversing biodiversity collapse.
Are carbon credits a scam? +
Many voluntary market credits (VCM) based on "avoided deforestation" are mathematically dubious. However, ex-post (verified, already sequestered) credits generated from strict domestic frameworks like the UK Woodland Carbon Code or Peatland Code represent real, measurable atmospheric carbon removal. We only model and advise on the latter.

The Herbivore Density Model

How many cattle should graze a 500-hectare site to maximise biodiversity? Our model calculates optimal Livestock Units (LU) per hectare based on soil type, seasonal growth curves, and target vegetation mosaics.

→ Open Model

Riparian Buffer Economics

Fencing off watercourses from livestock reduces phosphate pollution and improves salmonid spawning. But what is the cost per linear meter, and how does it offset water company catchment management tariffs?

→ Read Analysis

Start with the Data

Stop relying on marketing brochures for ecological restoration. Use our open-access models and data to build a rigorous business case for nature recovery.

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Navigating Statutory Grants

Private finance (BNG, Carbon) must be stacked with statutory grants for maximum yield. We model scenarios combining private natural capital sales with Countryside Stewardship and the incoming Environmental Land Management schemes (ELMs).

SFI (Sustainable Farming Incentive)

Low barrier to entry, highly flexible 3-year agreements focused on soil health and low-input grassland management.

Local Nature Recovery

Mid-tier funding for targeted interventions like wetland creation and riparian buffers.

Landscape Recovery

Bespoke, long-term (20+ year) agreements for large-scale (>500ha) collaborative rewilding projects.

Diagram showing succession from degraded pasture to broadleaf woodland

The Successional Diagram

Rewilding is fundamentally the management of ecological succession. Our models dictate that active intervention is required to move from degraded mineral soil pasture (State 1) to a structurally diverse scrub mosaic (State 2).

Without targeted disruption (e.g., pig rooting, targeted grazing), heavy ryegrass swards will resist colonisation by broadleaf saplings for decades.

Read the Methodology

Policy Briefings

We do not just model the current regulatory environment; we advocate for structural changes to natural capital markets to ensure ecological integrity and prevent greenwashing.

Comprehensive Index