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Practical guidance

Biodiversity-Related Environmental Risks

Understand biodiversity-related business risks by examining dependencies, impacts, locations and supply relationships before selecting credible actions.

EnvironmentalManagement.help editorial desk · Reviewed

Biodiversity-related environmental risks involve the relationship between an organisation and living systems. A business can affect habitats, species and ecosystem condition while also depending on services such as water supply, pollination or natural regulation. Understanding both directions helps prevent biodiversity from becoming a generic statement disconnected from operations.

The aspects and impacts overview explains how to assess interactions. The guide to risks and opportunities connects those findings with management decisions. Biodiversity assessment may require specialist knowledge, especially for site-specific ecological conclusions.

Distinguish impacts and dependencies

An impact concerns a change associated with the organisation’s activities or value chain. A dependency concerns something the organisation needs from nature or ecosystem functioning.

For example, an activity may affect water quality while also depending on a reliable water resource. An agricultural supply chain may depend on ecological processes and create pressures through land management or inputs.

These relationships can overlap but should not be merged into a single vague risk label. Clear descriptions help identify whether the response concerns preventing harm, managing supply exposure or both.

Begin with location and activity

Biodiversity questions are strongly influenced by place. Identify relevant sites, land use, surrounding habitats, water connections and activities before choosing actions.

A visually tidy or previously developed site is not necessarily ecologically irrelevant. Conversely, the presence of green space does not establish a particular biodiversity value without suitable assessment.

Use available credible information for screening and obtain competent ecological input where needed. Do not infer species absence from a brief walk or choose survey timing without appropriate expertise.

Follow environmental pathways

Potential pressures can arise through land disturbance, releases, resource use, light, noise or other interactions, depending on the activity and setting.

Describe the source, pathway and receptor where evidence allows. A statement such as harms biodiversity is too broad to explain what could change or how a control would help.

Coordinate biodiversity consideration with existing aspect assessments. Water, land and material interactions may already be recorded, but the ecological consequence or sensitivity may need clearer treatment.

Examine supply-chain connections

Relevant interactions can occur through raw materials, agricultural products, extraction, manufacturing or other purchased inputs. Identify important commodities and locations where information is available.

State the organisation’s influence realistically. A buyer may set specifications, seek traceability or engage suppliers without controlling every upstream practice.

Avoid treating a general supplier policy or product label as complete evidence for all biodiversity concerns. Understand what the evidence covers and where it leaves uncertainty. Targeted questions can be more useful than a long questionnaire with no follow-up process.

Understand policy context without inventing obligations

The Convention on Biological Diversity’s Global Biodiversity Framework includes Target 15 concerning measures for business assessment, disclosure and reduction of biodiversity-related risks and negative impacts.

That international policy context does not by itself establish identical direct legal duties for every business in every jurisdiction. Determine applicable local requirements, project conditions and commitments through the organisation’s own compliance process.

Keep voluntary commitments clear as well. Once an organisation adopts a commitment, it needs to understand its scope, evidence needs and responsibilities rather than use broad language that operations cannot support.

Prioritise investigation and action

Use the significance method and relevant technical evidence to identify important interactions. Consider scale, sensitivity, uncertainty and the organisation’s decision authority.

Where information is weak but potential consequences are serious, further investigation may be the first useful action. Do not fill the gap with an arbitrary low score.

Connect priorities with design, purchasing, land management, operating controls or supplier engagement. Ensure that actions address the identified relationship rather than a convenient activity unrelated to the main pressure.

Be careful with improvement claims

A planting project or habitat activity can be worthwhile, but its benefit depends on design, location, species suitability, maintenance and outcomes. Activity counts alone do not establish ecological improvement.

Do not claim that an unrelated positive project cancels all adverse impacts. Different locations, ecosystems and timescales can make such comparisons inappropriate or require specialised methods.

Define the baseline and evidence before making public claims. Distinguish an intention, an action completed and a demonstrated outcome. This protects both decision quality and the credibility of communication.

Monitor and review proportionately

Choose information that helps test the relevant relationship. This may involve operational measures, supplier evidence or specialist ecological monitoring, depending on the question.

Assign ownership and review triggers. Changes to sites, sourcing, processes or environmental knowledge can alter the assessment. Retain limitations so future reviewers understand what was actually established.

Biodiversity-related planning is useful when it connects nature with specific activities and decisions. It should make important dependencies and impacts visible, support competent assessment and lead to actions that can be explained through evidence rather than broad promises.

Bring procurement and site managers into the same review where their decisions affect a shared pressure. Separate reporting lines can otherwise leave a material interaction recognised by both teams but owned by neither.

Retain the location and scope of supporting ecological information. A conclusion about one area, season or supply source should not be extended automatically to another setting without checking whether the evidence remains relevant.

Sources and further reading

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