Double Materiality Assessment
for Agriculture

Double materiality assessment for Agriculture

Agriculture is one of the few sectors where all five ESRS environmental standards are routinely material. A European agri-food group with 800 employees, arable and livestock operations across 15,000 hectares, and EUR 120M revenue faces E1 through E5 before it considers social and governance topics. Methane from livestock, nitrous oxide from fertilised soils, ammonia emissions, nitrate leaching into groundwater, water abstraction for irrigation, habitat conversion from land use change, and soil depletion from intensive farming all trigger materiality under the ESRS 1.20-33 framework. The sector's direct dependence on natural capital makes the double materiality concept unusually intuitive here: agriculture affects the environment, and environmental degradation directly threatens agricultural productivity.

E1 Climate change is material through Scope 1 emissions from livestock (enteric fermentation, manure management), agricultural soils (N2O from fertiliser application), and machinery fuel use. The European Environment Agency estimates that agriculture accounts for 11% of total EU greenhouse gas emissions. Financial materiality comes from physical climate risk (drought, floods, heatwaves affecting crop yields) and transition risk (potential inclusion of agricultural emissions in carbon pricing mechanisms). E2 Pollution covers pesticide use, fertiliser runoff causing eutrophication, and ammonia emissions from livestock. The EU's Farm to Fork Strategy targets a 50% reduction in pesticide use by 2030, creating direct financial materiality through compliance costs. E3 Water and marine resources is material for irrigated agriculture, particularly in southern Europe where water stress is intensifying. E4 Biodiversity is material through land use change, pesticide impacts on pollinators, and habitat fragmentation from field consolidation. The EU Nature Restoration Regulation requires member states to restore degraded ecosystems, including farmland, by 2030. E5 Resource use covers soil health, nutrient cycling, and organic waste management. S1 Own workforce addresses seasonal labour conditions, migrant worker welfare, and health risks from pesticide exposure. S2 Workers in the value chain applies to farm labour in supply chains, particularly for entities sourcing from regions with documented forced or child labour in agriculture (the ILO estimates 112 million children work in agriculture globally). S3 Affected communities covers water access for communities near irrigated farms and pesticide drift affecting neighbouring populations.

Assurance providers find that agricultural entities frequently underassess E4 Biodiversity by treating it as an abstract ecological concern rather than scoring it against the specific criteria in ESRS 1.45-48. The irremediable character criterion (can the impact be undone?) is particularly relevant: species extinction and topsoil loss are irreversible on human timescales, which should push severity scores higher. A second finding is the failure to include Scope 3 emissions from purchased fertilisers and animal feed in the E1 assessment. These upstream emissions are often as large as direct agricultural emissions.

Agricultural entities should organise the assessment by farm type and product line. Arable operations generate different topics than livestock, aquaculture, or forestry. For each operation, use agronomic data (fertiliser application rates, pesticide usage records, water abstraction licences, livestock numbers) as evidence for environmental scoring. For social topics, use employment records, seasonal worker contract terms, health and safety incident data, and supply chain audit reports. The EU's Common Agricultural Policy (CAP) conditionality requirements and GAEC standards provide a useful cross-reference for environmental baseline compliance.