Carbon Sequestration & Sustainability Metrics

Planting, permeable surfaces, and water strategy each affect a site’s carbon, heat, and biodiversity outcomes — this tool estimates those figures.

Units
Project Details
Tree Planting
Ground Cover & Vegetation
Rate: 0.15 kg CO₂/m²/yr
0.55 kg/m²/yr
0.40 kg/m²/yr
0.25 kg/m²/yr
0.60 kg/m²/yr
0.80 kg/m²/yr
Soil Amendments (One-off)
×3.67×0.80 perm = kg CO₂e
500 kg/m³ × 0.50 × 0.50 humif.
Annual Carbon Breakdown
Tree Sequestration
–
kg CO₂/yr
Ground Cover
–
kg CO₂/yr
Soil Carbon (one-off)
–
kg CO₂e
Total over Design Life
–
tCO₂e
Rate per Area
–
kg CO₂/m²/yr
Equivalent Car-km Offset
–
km/yr
Equivalent Households
–
homes/yr
Carbon Market Value
Annual Offset Value
–
$/yr
Lifetime Offset Value
–
$
Rates: i-Tree Eco, FC Bulletin 48, USDA FS. Apply maturity (0.25–1.0×) and growth rate (0.8–1.2×) multipliers. Biochar permanence 0.80. Compost: 500 kg/m³ dry × 50% C × 50% humification × 3.67 CO₂:C.
Units
CO₂
Embodied Carbon Calculator
Full lifecycle embodied carbon analysis (A1–A5, B1–B6, C1–C4, D) for landscape materials, transport, construction, maintenance and end-of-life is available in the dedicated Embodied Carbon Calculator tool.
Open Embodied Carbon Calculator
Net Carbon Balance — Manual Entry
Paste totals from the Embodied Carbon tool to calculate net project carbon balance.
Whole-Life Carbon Balance
A1–A5 Materials & Construction
B1–B6 Maintenance & Operation
C1–C4 End of Life
D Biogenic Credits
Net Whole-Life Carbon
Net Carbon Status
The dedicated Embodied Carbon Calculator provides full RIBA 2030 / LETI benchmarking, phase-by-phase analysis, ICE Database v3.0 carbon factors and PDF/CSV export.
Units
Site Land Cover Composition
Total area elements. Total should not exceed site area.
Albedo 0.15
Albedo 0.25
Albedo 0.20
Albedo 0.06
Albedo 0.50
Albedo 0.05
Albedo 0.15
Context & Climate
Site Greenspace Ratio (SGR)
–
%
Tree Canopy Cover
–
% of site
Baseline Albedo
–
index
Design Albedo
–
index
ET Cooling Flux
–
MJ/m²/day
Cooling Energy Offset
–
kWh/yr est.
LEED v4.1 SSc5 — ≥ 20% canopy cover
BREEAM LE05 — Site Greenspace Ratio ≥ 40%
WHO Urban Green Space — ≥ 9 m²/resident
UHI Mitigation Rating
Each 10% increase in urban tree cover reduces peak temperature ~0.6–1.2°C (Bowler et al. 2010). Albedo gain of 0.1 to ~0.3°C surface cooling. Model is simplified for design-stage estimation.
Units
Baseline Habitats — Pre-Development
Proposed Habitats — Post-Development
Biodiversity Enhancement Features
+0.002 BU each
+0.003 BU each
+0.001 BU each
D=6×area/10000
D=5×0.7×length/1000
+0.001 BU each
Baseline Biodiversity Units
–
BU
Proposed Units
–
BU
Feature Bonus
–
BU
Total Post-Dev Units
–
BU
UK Mandatory BNG — ≥ 10% (Metric 4.0)
BREEAM LE 02 — Ecological Enhancement
Biodiversity Deficit / Off-site Credits
DEFRA Biodiversity Metric 4.0: BU = Area(ha) × Distinctiveness × Condition × Strategic Significance. Mandatory 10% BNG in England (Environment Act 2021). Off-site statutory credits required if on-site target cannot be achieved.
Units
Site Hydrology
15% interception
40% retention
Irrigation & Demand
Recycled Water Sources
80% retention
Total Annual Rainfall
–
m³/yr
Canopy Interception
–
m³/yr
Rainwater Harvest Yield
–
m³/yr
Net Irrigation Demand
–
m³/yr
Runoff Reduction
–
%
Irrigation Self-Sufficiency
–
%
Annual Cost Saving
–
$/yr
LEED WE — ≥ 50% irrigation self-sufficiency
BREEAM Wat 01 — water reduction ≥ 30%
Rainwater yield = min(imperm×0.85×rain/1000, tank×10/1000). Irrigation demand adjusted for drought-tolerant planting (up to 50% reduction) and system efficiency. Runoff reduction from interception, green roofs, SuDS and permeable paving.
Units
Project Context
Carbon & Climate
Link from Tab 1
Ecology & Biodiversity
Water & Materials
Score Ring + Breakdown
100 /100
Carbon & Climate–
Ecology & BNG–
Water–
Materials–
Certification Alignment
LEED Points (indicative)
–
pts
BREEAM Credits (indicative)
–
credits
Carbon Payback
–
years
Top 3 Improvement Opportunities
Certification thresholds: ≥80 = LEED Platinum/BREEAM Outstanding | 65–79 = Gold/Excellent | 50–64 = Silver/Very Good | 35–49 = Certified/Good. Scores are indicative; formal certification requires full audit.
Units
Site Areas
Ecosystem Service Unit Values — TEEB/CICES
Based on TEEB/CICES/i-Tree UK unit values. Adjust to local context.
Service Value Breakdown
Air Purification
–
Carbon Value
–
Stormwater
–
Cooling / Energy
–
Wellbeing / Amenity
–
Property Uplift (Cap)
–
Value per Area of Green Space
–
$/m²/yr
Property Value Uplift
–
$ capital
TEEB/CICES framework. Values are indicative for design iteration. Wellbeing and amenity values from landscape economics literature. Property uplift 3–15% for quality public realm. Adjust unit values to local market conditions.

How Landscapes Store Carbon, Cool Cities, and Support Biodiversity: The Numbers Explained

Sustainable landscape design has moved well beyond good intentions into a discipline that increasingly has to be quantified, reported, and benchmarked. This guide explains, in plain terms, how the most common sustainability metrics used in landscape and urban design are actually calculated, so you can understand and even estimate them yourself.

Estimating carbon sequestration from planting

Trees and shrubs draw down atmospheric carbon dioxide as they grow, storing carbon in woody biomass, roots, and eventually in soil organic matter. The amount of carbon a planting scheme sequesters over time depends on three main variables working together: the species chosen, since different trees have very different growth rates and eventual biomass, the planting density and total number of individuals, and the time horizon being assessed, because a young tree sequesters relatively little carbon in its early years and then accelerates as it matures before eventually plateauing. As a rough illustrative order of magnitude, a single moderately fast-growing urban tree can sequester somewhere in the range of twenty to forty kilograms of carbon dioxide per year once established, meaning a modest avenue planting of fifty trees can realistically draw down more than a tonne of carbon dioxide annually within a decade of establishment, entirely separate from any embodied carbon savings elsewhere in the scheme.

Understanding the Urban Heat Island effect and how canopy reduces it

Hard, dark surfaces such as asphalt and unshaded concrete absorb solar radiation during the day and re-radiate it as heat well into the evening, which is the core mechanism behind the Urban Heat Island effect that makes dense urban areas measurably warmer than surrounding vegetated land, sometimes by several degrees Celsius during summer evenings. Tree canopy interrupts this process in two ways, by shading hard surfaces so they absorb less solar radiation in the first place, and through evapotranspiration, the process by which trees release water vapour that cools the surrounding air much like natural evaporative cooling. As a general principle, increasing canopy cover and permeable, vegetated surface area at the expense of exposed hard paving is the single most effective landscape-scale intervention available for reducing local urban heat island impact.

What Biodiversity Net Gain actually measures

Biodiversity Net Gain works on the principle that a development or redesign should leave biodiversity measurably better off than it was before, rather than simply avoiding harm. In practice this is assessed by comparing a habitat baseline score, which accounts for the size, condition, and type of habitat present before works begin, against a post-development score reflecting the size, condition, and type of habitat created or retained afterward, with the difference expressed as a net gain or loss. Habitats are not treated as equal, meaning a small area of species-rich, well-connected habitat can outweigh a much larger area of low-value amenity grassland, which is why simply adding more green space does not automatically guarantee a strong biodiversity outcome unless habitat quality and diversity are genuinely improved.

How water sustainability is assessed

Water sustainability in landscape design generally compares the potable, mains-supplied water a scheme would need under a conventional design approach against the reduced demand achieved through interventions such as drought-tolerant and native planting selection, efficient irrigation methods, and rainwater harvesting that offsets irrigation demand with collected roof or hard-surface runoff. A reduction of thirty percent or more in potable water demand compared to a conventional baseline design is a commonly referenced threshold in international green building certification schemes, and is a realistic target for a well-designed planting and irrigation strategy working together rather than either measure alone.

How these metrics map onto recognised certification frameworks

Two of the most widely used sustainability certification frameworks internationally are BREEAM, the Building Research Establishment Environmental Assessment Method, and LEED, Leadership in Energy and Environmental Design. Both frameworks reward exactly the categories of improvement described above, including ecological enhancement, site greenspace ratio, and reductions in potable water demand, through their own scoring credits, with performance typically banded into tiers that roughly correspond across the two systems, such as an entry-level pass, a good or silver performance, an excellent or gold performance, and an outstanding or platinum performance at the very top. Understanding roughly where a scheme’s raw sustainability numbers would land within these bands is genuinely useful for early client conversations, even though a full certification submission requires far more detailed, verified, project-specific evidence than any general calculation can provide.

Disclaimer

The information and any results referenced on this page are provided for general educational and early design exploration purposes only. References to BREEAM and LEED scoring bands are illustrative comparisons and do not represent an official assessment, certification, or endorsement by either organisation. Actual sustainability outcomes depend on detailed site conditions, long-term maintenance, local climate, and verified data collection. For any formal certification, environmental reporting, or planning submission, consult a qualified sustainability consultant or the relevant certifying organisation.