Screening, Scoping and Terms of Reference

Introduction

Environmental Impact Assessment (EIA) is most effective when effort is directed toward the environmental and social issues that can materially influence project decisions. Screening, scoping and the preparation of Terms of Reference (ToR) are the stages that establish this direction. They occur before detailed baseline studies and impact prediction, but they strongly influence the quality, cost and credibility of the entire assessment.

Screening determines whether a proposed project requires an EIA and, where assessment is required, what level or type is proportionate. Scoping identifies the important issues, affected people, valued environmental and social components (VECs), alternatives, boundaries and methods that should be examined. The Terms of Reference convert the results of screening and scoping into a clear assignment for the EIA team.

Poor screening may subject minor activities to unnecessary procedures or allow significant impacts to escape assessment. Poor scoping may produce a large report that contains extensive irrelevant information but fails to examine the issues that matter. Weak ToR create uncertainty about responsibilities, methods, deliverables and standards. For construction professionals, competence in these stages is essential because project design, procurement, scheduling, land acquisition, community relations and regulatory approval are all affected by early EIA decisions.

Learning Objectives

By the end of this chapter, students should be able to:

1. Explain the purpose and relationship of screening, scoping and ToR.
2. Apply screening criteria to determine whether an EIA, partial assessment or no formal assessment is appropriate.
3. Identify VECs and distinguish valued components from general environmental information.
4. Define appropriate spatial, temporal and administrative boundaries.
5. Establish transparent significance criteria and prioritize impacts.
6. Prepare a proportionate, legally defensible and practically useful ToR.
7. Recognize public participation, professional ethics, uncertainty and governance requirements in early EIA.

1. The Position of Screening, Scoping and ToR in the EIA Process

EIA is not simply the production of an environmental report. It is a decision-support process that connects a proposed action with possible changes in the environment and society. A simplified sequence is:

Project concept → screening → scoping and consultation → ToR → baseline studies and impact assessment → alternatives and mitigation → EIA report → review and decision → monitoring and follow-up.

The sequence is iterative rather than strictly linear. For example, a preliminary field visit may reveal a wetland that changes the screening decision. Consultation may identify a culturally important site that requires a broader study area. Preliminary design may show that an apparently minor road project will require significant land acquisition. Accordingly, screening and scoping should be revisited when material new information becomes available.

Figure: Relationship between screening, scoping and the Terms of Reference.

2. Screening: Deciding the Level of Assessment

2.1 Purpose

Screening answers three related questions:

• Is the proposal included in the jurisdiction's EIA system?
• Is the project likely to cause significant adverse environmental or social effects?
• What level of assessment is proportionate to the risk and uncertainty?

Screening should take place early enough to influence project selection and design, but with enough information to make a defensible decision. It should not be treated as a purely administrative formality.

2.2 Common screening systems

Most systems use one or a combination of the following approaches.

Mandatory thresholds may involve land area, production capacity, reservoir volume, road length, waste quantity, emissions or investment value. Thresholds are screening devices, not guarantees that impacts will be insignificant. A small project in a sensitive wetland, protected area, densely populated settlement or culturally significant landscape may require detailed assessment despite its size.

2.3 Screening criteria

A robust screening decision considers at least the following factors:

Project characteristics. These include scale, construction methods, resource consumption, hazardous materials, waste streams, emissions, duration, reversibility and the potential for accidents.

Location and sensitivity. Important questions concern protected areas, wetlands, floodplains, groundwater recharge zones, steep or unstable slopes, critical habitats, heritage places, indigenous or traditional territories, dense settlements and areas with existing pollution or social conflict.

Impact characteristics. Consider magnitude, geographic extent, duration, frequency, reversibility, probability, direct and indirect pathways, cumulative effects and the vulnerability of affected receptors.

Alternatives and design. A project may be screened differently after a change in alignment, technology, site, construction method or operating capacity.

Legal and institutional requirements. The screening decision must comply with applicable EIA legislation, planning law, building regulations, pollution controls, labour requirements, land and cultural heritage law, and any lender or international standards that apply.

2.4 Categories of screening outcome

Although terminology varies, common outcomes include:

1. No formal EIA required, subject to standard permits and environmental conditions.
2. Preliminary or limited assessment, for projects with localized, predictable and manageable impacts.
3. Full EIA, for projects with potentially significant, diverse, irreversible, cumulative or uncertain effects.
4. Redesign, relocation or rejection at an early stage, where impacts are unacceptable or the project is inconsistent with planning or protected-area requirements.

A screening record should identify the proposal, proponent, location, data sources, criteria applied, uncertainties, decision, conditions and responsible authority. Reasons are as important as the conclusion because they support transparency, appeal and later review.

3. Scoping: Focusing the Assessment

3.1 Meaning and purpose

Scoping is the systematic process of deciding what the EIA should study and how it should study it. It prevents two common errors:

• Under-scoping: important effects, affected groups or alternatives are omitted.
• Over-scoping: time and resources are spent on issues that cannot influence the decision.

Scoping is both technical and participatory. Desktop studies, mapping, site reconnaissance and preliminary impact pathways provide technical evidence. Consultation with communities, regulators, specialists, local government and civil society reveals values, historical experience and concerns that may not appear in official datasets.

3.2 From project activities to impact pathways

A useful scoping method begins with project activities and follows cause-and-effect pathways:

Activity → stressor or pressure → environmental change → exposure → effect on a receptor or VEC.

For example:

• vegetation clearing → sediment runoff → increased turbidity → exposure of aquatic habitat → reduced fish spawning success;
• pile driving → underwater noise → disturbance → exposure of sensitive species → altered movement or breeding;
• worker influx → pressure on housing and services → increased rents and demand → effects on low-income households;
• traffic diversion → increased travel time and dust → exposure of roadside residents → health and livelihood effects.

The pathway must be plausible and supported by evidence. A list of generic topics is not a substitute for analysis.

3.3 Valued environmental and social components

A VEC is an environmental or social feature considered important by specialists, affected communities, authorities or broader society, and potentially affected by the project. Examples include:

• surface-water quality and quantity;
• groundwater and recharge areas;
• wetlands, forests and critical habitat;
• threatened species and ecological connectivity;
• soil stability and erosion control;
• landscape character and visual amenity;
• cultural heritage and sacred places;
• public health and safety;
• livelihoods, access and income;
• housing, services and community cohesion;
• labour conditions and worker welfare;
• gender equality and vulnerable groups.

VEC identification should not be based only on what can be easily measured. Cultural meaning, customary use, fear, dignity, distributional fairness and future generations may be important even where quantitative data are limited.

A practical VEC register records the component, why it is valued, its current condition, the people or ecosystems dependent on it, potential stressors, indicators, spatial extent, seasonal variation, data gaps and proposed assessment method.

3.4 Alternatives in scoping

Scoping should establish which alternatives will be compared. At minimum, these may include:

• the proposed design or alignment;
• alternative sites, routes, technologies or construction methods;
• different scales or phasing arrangements;
• demand-management or non-project alternatives;
• the no-project alternative.

The no-project alternative is not necessarily a recommendation against development. It provides a reference condition for understanding what would happen without the proposal, including both avoided impacts and foregone benefits.

4. Defining Spatial and Temporal Boundaries

4.1 Spatial boundaries

The study area should correspond to impact pathways, not merely property boundaries. Different VECs often require different boundaries. A construction site may define the direct footprint, while a river basin may be needed for downstream water effects. A labour study may require nearby towns and worker-origin areas, whereas a traffic assessment may cover the road network affected by construction vehicles.

Important spatial concepts include:

• Project footprint: land or water directly occupied or disturbed.
• Zone of influence: area potentially affected by direct, indirect or induced effects.
• Ecological boundary: habitat, watershed, airshed or species range relevant to the pathway.
• Social study area: communities, service areas, livelihood zones and administrative units affected by the project.
• Cumulative-effects area: geographic area in which effects of multiple projects or activities overlap.

Maps should show the project, settlements, land uses, sensitive receptors, ecological features, infrastructure, administrative boundaries and proposed study areas. Boundaries must be explained and revised where evidence indicates that impacts extend beyond them.

4.2 Temporal boundaries

Temporal scope covers more than the construction period. It should consider:

1. pre-construction activities, including land acquisition and workforce mobilization;
2. construction, including peak traffic, clearing and temporary facilities;
3. operation and maintenance;
4. decommissioning, closure or rehabilitation;
5. accidents, emergencies and abnormal conditions;
6. cumulative development over a reasonable planning horizon;
7. seasonal and interannual variability.

A baseline is not simply a single date. For example, wet-season and dry-season water quality may differ substantially. Migratory species, agricultural cycles, tourism seasons and school calendars can also affect impact significance and consultation timing.

5. Significance and Prioritization

5.1 Meaning of significance

Impact significance is a reasoned judgment about the importance of a predicted change. It is not identical to magnitude. A moderate change in a highly vulnerable wetland may be more significant than a larger change in a resilient, low-value area.

Typical significance considerations are:

• magnitude or intensity;
• extent;
• duration and frequency;
• reversibility and recoverability;
• probability;
• sensitivity, vulnerability or value of the receptor;
• legal standards and policy objectives;
• distributional effects and equity;
• stakeholder concern;
• cumulative and transboundary effects;
• confidence in the evidence.

A transparent assessment distinguishes the impact before mitigation, the residual impact after mitigation, and the uncertainty associated with each conclusion.

5.2 Significance matrices

A matrix can support consistency, but it must not replace professional reasoning. A simple qualitative matrix may classify receptor sensitivity as low, medium or high and impact magnitude as low, medium or high. The resulting priority may be low, moderate or high. The criteria must be defined in the ToR, and the assessment should explain borderline judgments.

Legal limits are not the sole measure of significance. An effect below a regulatory limit may still be important if it is concentrated among vulnerable households, affects a culturally significant site or contributes to cumulative deterioration. Conversely, a temporary exceedance during an emergency may require a different interpretation from a continuous exceedance during normal operation.

5.3 Uncertainty and precaution

Early-stage decisions are made with incomplete information. Uncertainty may concern project design, baseline conditions, climate variability, exposure pathways, receptor response or the effectiveness of mitigation. The ToR should therefore require explicit assumptions, data-quality statements, sensitivity analysis where appropriate, and monitoring commitments.

Where potential harm is serious or irreversible and evidence is uncertain, precaution supports further investigation, avoidance, conservative assumptions or adaptive management. Precaution does not mean that every hypothetical effect must be treated as certain; it requires a rational response to uncertainty and risk.

6. Preparing the Terms of Reference

6.1 Function of the ToR

The ToR is the controlling document for the EIA study. It communicates what must be investigated, the standards and methods to be used, the required consultation, the outputs expected and the basis on which the study will be reviewed. It should be specific enough to guide the team but flexible enough to accommodate justified changes arising from new evidence.

6.2 Recommended contents

A proportionate ToR normally includes:

1. Purpose and decision context: approvals sought, decisions to be informed and relationship to planning or procurement.
2. Project description: location, components, design capacity, construction sequence, materials, energy and water demand, emissions, wastes, workforce, schedule and decommissioning.
3. Legal and institutional framework: applicable laws, permits, standards, policies, treaties, lender requirements and responsible authorities.
4. Alternatives: design, site, alignment, technology, scale, phasing and no-project alternatives.
5. Screening and scoping rationale: key issues, excluded issues and reasons for prioritization.
6. Baseline requirements: methods, indicators, sampling locations, quality assurance, seasonal coverage and data sources.
7. Impact assessment methods: prediction, significance criteria, uncertainty, cumulative effects, accidents, climate risks and residual impacts.
8. Social assessment: land acquisition, displacement, livelihoods, labour, gender, vulnerable groups, health, safety, cultural heritage and community services.
9. Mitigation hierarchy: avoidance, minimization, restoration or rehabilitation, and offsetting only where appropriate and legally permitted.
10. Stakeholder engagement: stakeholder identification, disclosure, accessible communication, consultation records, grievance mechanisms and responses to comments.
11. Environmental and social management: mitigation measures, responsibilities, schedule, indicators, monitoring, reporting, training and corrective action.
12. Deliverables and review: report structure, maps, data tables, non-technical summary, disclosure requirements, submission format, timetable and quality control.
13. Team qualifications: required disciplines, independence, local knowledge and conflict-of-interest declarations.

6.3 Proportionality

A ToR should match the level of risk, complexity and uncertainty. A small urban drainage improvement may need focused hydrology, traffic, construction nuisance and community-safety studies. A major transport corridor may require biodiversity, resettlement, induced development, climate resilience, cumulative effects, cultural heritage and regional economic analysis.

Proportionality does not mean lowering standards for disadvantaged communities or ignoring difficult issues. It means allocating effort according to potential significance and decision relevance. The ToR should state which matters are low priority, but allow them to be revisited if new evidence emerges.

6.4 Quality-control questions

Before issuing a ToR, the preparer should ask:

• Are all project phases and realistic alternatives covered?
• Are direct, indirect, induced and cumulative effects considered?
• Does the study area follow impact pathways?
• Are vulnerable people and non-human receptors represented?
• Are baseline methods technically adequate and seasonally appropriate?
• Are significance criteria explicit and legally compatible?
• Are consultation and disclosure accessible and meaningful?
• Are mitigation responsibilities and monitoring requirements clear?
• Can the final report be reviewed against the ToR?
• Does the ToR avoid demanding information that cannot influence the decision?

7. Applied Case: Illustrative Urban Bypass Project

Background

A municipality proposes a 12-kilometre bypass to reduce congestion in the central district. The initial concept crosses agricultural land, a seasonal wetland and the edge of two villages. Construction would require borrow material, temporary worker accommodation and relocation of a small number of roadside businesses.

Screening decision

The project exceeds the jurisdiction's road-length threshold for formal EIA. In addition, the wetland, land acquisition and potential induced development create site-specific sensitivity. Screening therefore requires a full EIA rather than a limited construction permit. The screening record identifies the need to examine alternatives before the alignment is finalized.

Scoping analysis

The preliminary activity–pathway review identifies the following priority VECs:

Scoping rejects a detailed study of offshore impacts because there is no plausible pathway, but retains climate resilience because flooding could affect road performance and downstream communities.

Boundaries and ToR

The hydrology study area follows the wetland catchment and downstream drainage channel. The social study area includes the two villages, roadside businesses and households whose access may change. The traffic area includes connecting roads likely to receive diverted or induced traffic. Baseline surveys must cover both wet and dry seasons, and consultation must occur before the alignment and resettlement plan are fixed.

The ToR requires comparison of the proposed route with a western alignment, a reduced-footprint design and the no-project alternative. It also requires avoidance of the wetland where feasible, replacement of lost access, safe pedestrian crossings, a livelihood-restoration program, dust and noise controls, a chance-find procedure, flood-resistant drainage and monitoring during construction and operation.

Outcome and learning points

The case illustrates that screening is influenced by both project category and receiving-environment sensitivity. Scoping converts general concerns into VECs, pathways, boundaries and methods. The ToR then makes these commitments auditable. It also shows why social and ecological issues should be considered together: changing an alignment to avoid habitat may alter land acquisition, traffic and livelihood effects elsewhere.

8. Participation, Ethics and Governance

Public participation is a source of knowledge and a matter of procedural fairness. Consultation should begin during scoping, not after all important decisions have been made. Information should be understandable, timely and available in relevant languages and formats. Meetings alone may exclude people who work, have disabilities, lack transport or fear speaking publicly. Suitable approaches may include household visits, focus groups, women-only discussions where appropriate, accessible venues, visual materials and confidential channels for sensitive concerns.

Participation does not give every participant a veto, nor does it permit a proponent to manufacture consensus. The professional obligation is to record concerns accurately, explain how they were considered and disclose unresolved disagreements.

Ethical practice requires independence, competence, honesty about uncertainty and avoidance of conflicts of interest. Consultants should not promise approval, suppress inconvenient data or define a narrow study area solely to reduce costs. Regulators must apply criteria consistently and provide reasons for decisions. Developers must provide sufficient information and resources for a credible assessment without directing conclusions.

Screening and scoping also involve distributional justice. Benefits and burdens may fall on different groups. A project that improves regional mobility but displaces low-income households requires more than an aggregate cost–benefit argument; it requires attention to rights, compensation, restoration and fair participation.

9. Technology, Data and Contemporary Practice

Geographic Information Systems (GIS), remote sensing, mobile data collection, acoustic sensors, automated air-quality instruments and digital consultation platforms can improve screening and scoping. GIS can overlay project footprints with wetlands, settlements, protected areas, flood risk and infrastructure. Remote sensing can reveal seasonal land-cover changes, but field verification remains necessary.

Artificial intelligence can assist with document review, map classification, complaint analysis and identification of possible impact pathways. However, AI outputs may reproduce biased or incomplete datasets, obscure reasoning and misclassify culturally important locations. AI should support—not replace—qualified professional judgment, local knowledge, verification, data protection and transparent documentation. Sensitive cultural, household or geolocation data require careful access controls.

Contemporary ToR increasingly address climate change, disaster risk, nature-based solutions, biodiversity loss, supply-chain impacts, circular construction, worker welfare and cumulative regional development. These additions should remain connected to decision needs rather than becoming unstructured lists of fashionable topics.

10. Challenges and Limitations

Several recurring challenges affect early EIA stages:

• Incomplete project definition: uncertain design makes impact prediction difficult. The response is to use design envelopes, alternatives and explicit assumptions.
• Threshold dependence: legal lists may miss sensitive small projects. Case-by-case sensitivity checks are essential.
• Data scarcity: baseline gaps should lead to targeted surveys and uncertainty statements, not invented precision.
• Consultation fatigue: repeated consultations without visible response reduce trust. Engagement should be coordinated and feedback should be reported.
• Scope creep: new issues can overwhelm the study. Use significance criteria and document why matters are included or excluded.
• Political or commercial pressure: independent review, public records and conflict declarations strengthen credibility.
• Cumulative effects: several individually modest projects may create substantial regional change. The assessment area and time horizon may need expansion.
• Changing climate and design: adaptive ToR and monitoring triggers allow management to respond to new information.

Best-Practice Principles

1. Screen early, but update the decision when material information changes.
2. Use both project thresholds and receiving-environment sensitivity.
3. Trace impacts through credible cause-and-effect pathways.
4. Define VECs through scientific evidence and stakeholder values.
5. Make spatial and temporal boundaries pathway-based and VEC-specific.
6. State significance criteria before conclusions are formed.
7. Compare reasonable alternatives, including the no-project alternative.
8. Make the ToR proportionate, measurable and reviewable.
9. Treat uncertainty, cumulative effects and vulnerable groups explicitly.
10. Use technology to improve evidence while retaining human accountability.

Chapter Summary

Screening determines whether a project requires an EIA and selects a proportionate level of assessment. It should consider project characteristics, location sensitivity, likely impact pathways, alternatives, legal requirements and uncertainty. Scoping then focuses the assessment by identifying VECs, alternatives, stakeholders, impact pathways, spatial boundaries and temporal boundaries. Significance depends on more than magnitude; duration, extent, reversibility, probability, receptor sensitivity, legal context, equity, cumulative effects and uncertainty are also relevant.

The Terms of Reference translate screening and scoping into an accountable study plan. A strong ToR describes the project, legal framework, alternatives, baseline methods, impact-prediction approach, significance criteria, stakeholder engagement, mitigation hierarchy, management and monitoring requirements, deliverables and team qualifications. Effective early-stage EIA is proportionate but not superficial, participatory but evidence-based, and flexible enough to respond to new information. For construction professionals, these stages provide the foundation for legally compliant design, responsible procurement, effective mitigation and socially legitimate project delivery.

Key Terms

Screening: The process of deciding whether an EIA is required and what level of assessment is appropriate.

Scoping: The process of identifying important issues, alternatives, boundaries, methods and stakeholders for an EIA.

Terms of Reference: A document specifying the purpose, scope, methods, outputs and quality requirements of an EIA study.

Valued Environmental and Social Component (VEC): An environmental or social feature considered important and potentially affected by a project.

Impact pathway: The cause-and-effect connection from a project activity to a stressor, environmental change, exposure and receptor effect.

Project footprint: The area directly occupied or disturbed by a project.

Zone of influence: The area potentially affected by direct, indirect or induced project effects.

Baseline: The existing environmental and social conditions against which change is assessed.

Significance: A reasoned judgment about the importance of an impact.

Magnitude: The intensity or scale of an environmental or social change.

Sensitivity: The susceptibility or value of a receptor affected by change.

Cumulative effects: Combined effects of the project with other past, present or reasonably foreseeable activities.

Residual impact: The impact remaining after mitigation.

Mitigation hierarchy: The sequence of avoidance, minimization, restoration or rehabilitation, and appropriate offsetting.

No-project alternative: The scenario describing likely conditions if the proposed project is not implemented.

Precautionary approach: Taking proportionate protective action where potential serious harm is uncertain.

Stakeholder engagement: A structured process of informing, consulting and responding to people and organizations affected by or interested in a project.

Adaptive management: Adjusting mitigation or operations in response to monitoring, learning and changing conditions.

Screening record: The documented evidence and reasoning supporting a screening decision.

Review Questions

Short Answer Questions

1. What are the main purposes of screening in EIA?
2. Define a valued environmental and social component and give two examples.
3. Why should spatial boundaries be based on impact pathways rather than only on the project footprint?
4. Distinguish between an impact before mitigation and a residual impact.
5. Identify four typical contents of a Terms of Reference.

Long Answer Questions

1. Explain the relationship between screening, scoping and Terms of Reference, and discuss how weakness at one stage can affect the rest of the EIA process.
2. Discuss the factors that should be considered when determining impact significance.
3. Explain how public participation can improve the technical and ethical quality of scoping.
4. Describe how alternatives should be addressed in an EIA ToR.
5. Discuss the advantages and limitations of using GIS, remote sensing and artificial intelligence in early EIA stages.

Analytical / Application Questions

1. A proposed 5-kilometre access road is below the statutory length threshold but crosses a wetland and borders a settlement. Recommend a screening outcome and justify it using project and receiving-environment criteria.
2. Develop a preliminary VEC register for a construction project that may affect groundwater, local businesses and a nearby heritage site. For each VEC, identify a likely pathway, study boundary and baseline requirement.
3. Critique a ToR that requires extensive air-quality modelling but says nothing about land acquisition, pedestrian safety or cumulative traffic. Explain how you would revise it and why.

Multiple Choice Questions with Answers

Question 1

What is the primary purpose of EIA screening?

A. To prepare the final environmental management plan

B. To determine whether assessment is needed and at what level

C. To calculate the project's construction cost

D. To select the contractor

Correct Answer: B. To determine whether assessment is needed and at what level

Question 2

Which factor can justify detailed assessment of a relatively small project?

A. The project has a short construction schedule

B. The project uses standard equipment

C. The project is located in a highly sensitive wetland

D. The project has a small office staff

Correct Answer: C. The project is located in a highly sensitive wetland

Question 3

Which sequence best represents an impact pathway?

A. Budget → contract → invoice → payment

B. Activity → stressor → environmental change → receptor effect

C. Survey → tender → award → completion

D. Policy → meeting → approval → procurement

Correct Answer: B. Activity → stressor → environmental change → receptor effect

Question 4

Which statement best defines a VEC?

A. Any item listed in a construction bill of quantities

B. A feature valued and potentially affected by the project

C. Only a species protected by international law

D. A temporary construction facility

Correct Answer: B. A feature valued and potentially affected by the project

Question 5

Why may a hydrological study area extend beyond a project boundary?

A. Water impacts can follow a catchment or downstream pathway

B. All EIA maps must cover an entire country

C. Project boundaries are never legally relevant

D. Hydrology is unrelated to project location

Correct Answer: A. Water impacts can follow a catchment or downstream pathway

Question 6

Which item should normally be included in a Terms of Reference?

A. A guaranteed approval date

B. The consultant's preferred contractor

C. Baseline methods and significance criteria

D. A promise that no impacts will occur

Correct Answer: C. Baseline methods and significance criteria

Question 7

Which statement about significance is most accurate?

A. Significance depends only on impact magnitude

B. Any legally permitted effect is insignificant

C. Significance also considers receptor sensitivity, duration, probability and equity

D. Stakeholder concerns must never influence significance

Correct Answer: C. Significance also considers receptor sensitivity, duration, probability and equity

Question 8

What is the correct order in the mitigation hierarchy presented in the chapter?

A. Offset, restore, minimize, avoid

B. Avoid, minimize, restore or rehabilitate, then consider offsetting where appropriate

C. Monitor, compensate, design, construct

D. Construct, operate, abandon, offset

Correct Answer: B. Avoid, minimize, restore or rehabilitate, then consider offsetting where appropriate

Question 9

Why is the no-project alternative useful?

A. It guarantees that the project will be rejected

B. It provides a reference for understanding avoided impacts and foregone benefits

C. It removes the need for baseline studies

D. It applies only to private projects

Correct Answer: B. It provides a reference for understanding avoided impacts and foregone benefits

Question 10

What is an appropriate use of artificial intelligence in early EIA?

A. Replacing all field verification and professional judgment

B. Making an approval decision without documented reasoning

C. Assisting document review or map classification subject to verification

D. Publishing confidential household locations openly

Correct Answer: C. Assisting document review or map classification subject to verification