In this section you will learn methods of conducting a quick assessment of the planned projects and developments to decide if their impacts on the environment and well-being are severe enough to develop a full EIA.
What is screening?
Screening is the first stage of the EIA process which results in a key EIA decision, namely to either conduct the assessment (based on the likely significant impacts) or not conduct it (in the anticipated absence of such impacts).
Screening is the first stage of the EIA process which results in a key EIA decision, namely to either conduct the assessment (based on the likely significant impacts) or not conduct it (in the anticipated absence of such impacts). Screening needs to follow specific procedures often described in the legislation so all the projects follow the same process.
Key contributions of screening to a good EIA:
- Facilitates informed decision making by providing clear, well-structured, factual analysis of the effects and consequences of proposed actions.
- Influences both project selection and policy design by screening out environmentally and/or socially unsound proposals, as well as modifying feasible action.
Why conduct screening?
An essential aspect of conducting an EIA is to determine the level of impact of the proposed project, development or initiative.
An essential aspect of conducting an EIA is to determine the level of impact of the proposed project, development or initiative. When we look at major development projects—especially those involving natural resources, such as mining, hydroelectric dams, or oil extraction—we can say for certain that they will require an environmental and social impact assessment. On the other hand, while the development of a tourism project may seem low-risk at first, a second look could reveal that the project requires large amounts of drinking water, energy, the removal of endangered flora or fauna, and will result in extensive sewage production. It may also lead to increased road and air traffic to deliver supplies, visitors and workers. Finally, the impacts of project could change over time. Thus, during the screening step as well as the whole EIA process, impacts are considered over the lifetime of the project, from the construction phase through to operations and after closing.
Most proposals can be screened very quickly because they will have few impacts and will be screened out of the EIA process. Only a limited number of proposals, usually large-scale projects, require a full EIA because they will likely have major irreversible impacts on environmental resources or on people’s health, livelihoods or cultural heritage. However, many projects with medium impacts will require an Environmental Management Plan (EMP) which is a component of a full EIA. EMPs are further described in Step 4: Impact Management.
What approaches exist?
Development BanksCentral AmericaMost countries in Central America focus on identifying the types of projects, their size and potential impacts to determine the need for an EIA.
Most countries in Central America focus on identifying the types of projects, their size and potential impacts to determine the need for an EIA. Overall, we can distinguish two different approaches to screening (United Nations University, UNEP, RMIT, 2007):
- Prescriptive or standardized approaches – Categories for different types of development proposals are outlined in legislation and regulations. Proponents can often decide whether their project will need an EIA based on these standardized approaches. These could include:
- Legal (or policy) definitions of proposals to which EIA does or does not apply.
- Inclusion lists of projects (with or without thresholds) for which an EIA is automatically required.
- Exclusion lists of activities that do not require an EIA because they are insignificant or are exempt by law (e.g., national security or emergency activities).
- Customized approaches – Proposals are screened on an individual or case-by-case base, using indicative guidance with categories.
Different countries and international agencies combine these types of screening procedures. Most often, a simple categorization (such as A – C or 1 – 3) is used. These categories help proponents and licensing agencies decide when a full EIA is needed.
- For high-impact projects: A full EIA is required because these are likely to have significant serious adverse environmental impacts (i.e., result in irreversible damage, affect vulnerable ethnic minorities, involve involuntary resettlement, or affect cultural heritage sites). These often include:
- Dams and reservoirs.
- Forestry and production projects.
- Industrial plants (large-scale).
- Irrigation, drainage, and flood control (large-scale).
- Mining and mineral development (including oil and gas).
- Port and harbour development.
- Reclamation, resettlement and new land development.
- Thermal and hydropower development;
- Manufacture, transportation, and use of pesticides and other hazardous and/or toxic materials.
- For medium-impact projects (those likely to have adverse environmental impacts that are less significant than those of in the previous category): Normally a limited EIA will be undertaken to identify suitable mitigation and management measures, and incorporate them into the project. These often include:
- Agro-industries
- Electrical transmission; rural electrification
- Aquaculture, irrigation and drainage (small-scale)
- Renewable energy
- Tourism
- Rural water supply and sanitation
- For low-impact projects (Those that are likely to have minimal or no adverse environmental impacts): No EIA is required. For example:
- Construction of small buildings
- Community garden development
- Development of wells in a community
- Outdoor recreation
Development BanksExamples of different types of screening categories within selected Development Banks
Examples of different types of screening categories within selected Development Banks | ||
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Types of screening | Details on types of screening | |
Inter-American Development Bank (IDB) | Project categories-A, B, C, and Uncategorized – According to the scale of the project, location, sensitivity and potential impact. | Category C – No EIA required, but some Category C operations may require specific safeguards or monitoring requirements to address environmental and other risks (social, disaster, cultural, health and safety etc.). Category B – Projects require an environmental and/or social analysis, according to, and focusing on, the specific issues identified in the screening process, and an environmental and social management plan (ESMP). Category B if its potential adverse environmental impacts on humans or environmentally important areas- including wetlands, forests, grasslands, and other natural habitats-are less adverse than those of Category A projects. Category A – Projects likely have significant adverse environmental impacts that are sensitive, diverse, or unprecedented. These impacts may affect an area broader than the sites. Potential impacts are considered “sensitive” if they may be irreversible (e.g., lead to loss of a major natural habitat) or raise impacts on indigenous peoples; natural habitats; physical and cultural resources; or/and involuntary resettlement. |
World Bank | Three categories, depending on the type, location, sensitivity, and scale of the project and the nature and magnitude of its potential environmental impacts. | Category A: Projects likely to have significant adverse environmental impacts that are sensitive, diverse, or unprecedented. These impacts may affect an area broader than the sites or facilities subject to physical works. EIA examines the potential negative and positive environmental impacts, compares them with those of feasible alternatives (including the “without project” scenario), and recommends any measures needed to prevent, minimize, mitigate, or compensate for adverse impacts and improve environmental performance. The proponent is responsible for preparing an EIA report. Category B: Proposed project can have potential adverse environmental impacts on human populations or environmentally important areas, but less adverse than those of Category A projects. These impacts are site-specific; few if any of them are irreversible; and in most cases mitigating measures can be designed more readily than for Category A projects. The scope of EA for a Category B project may vary from project to project, but it is narrower than that of Category A EIA. Category C: A proposed project is likely to have minimal or no adverse environmental impacts. Beyond screening, no further EA action is required. |
European Union | Case-by-case examination based on lists of sectors and types of activities that require an EIA and a set of activities that may require EIA depending on their location, activities, and impacts. | Decided according to thresholds and/or criteria (for example size), location (sensitive ecological areas in particular) and potential impact (surface affected, duration). Member States may set thresholds or criteria for the purpose of determining which of such projects should be subject to assessment on the basis of the significance of their environmental effects such as:- For power stations: capacity in MW – For landfills: total volume, volume/day, tonnes/day, total capacity in tonnes- For shopping centres: area in hectares or m2 (area, floor space) – For roads: length of road (in km) Specific project are listed, including crude-oil refineries, thermal power stations and other combustion installations, installations for the extraction of asbestos, chemical installations, groundwater abstraction, works for the transfer of water resources between river basins, dams, extraction of petroleum and natural gas, pipelines for the transport of gas, intensive rearing of poultry or pigs, quarries and open-cast mining. |
Source: IDB, 2011; World Bank , 1999; European Union, 2001.
Central AmericaApproaches to screening in selected countries in Central America
Approaches to screening in selected countries in Central America | |||
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Country | Project types | Criteria | Details |
Belize | Regulations list the types of projects that require, do not require, and may require EIA, depending on size and location. Proponents should apply early to the government agency to determine whether project requires an EIA or EMP. | ||
Costa Rica | X | X | Two-stage screening: (i) legislation lists the type of activities, projects, and works that require EIA; and (ii) application of Form D1 or Form D2, depending on project category. |
Dominican Republic | X | X | Law defines the types of projects, works, and activities that require EIA (and determines the type of study required for each category) according to the potential environmental impact; for projects not included in the list, national agency determines if an EIA is needed. |
Ecuador | X | Legislation defines the type of projects that require an EIA. Proponents must register the project in the online Environmental System (SUIA), to request a certification of the project’s location in relation to conservation areas and forest protected areas. | |
El Salvador | X | Legislation defines the type of projects that require an EIA. Group A: does not require the presentation of any information Group B-1: EMP Group B-2: EIA. | |
Guatemala | X | Regulation lists different types of activities that require an EIA, including hotels of a certain size, marinas, desalination plants, hydroelectric projects, and coastal development. | |
Honduras | X | X | Law and regulations list the types of projects and activities that require an EIA; Category 1: SINEIA F-01 form and Category 2 or 3: SINEIA F-02 form and Environmental Management Plan Category 4: EIA. Four categories (1, 2, 3, and 4) based on the characteristics of operation, nature of the actions, its potential environmental impacts or risk. |
Mexico | X | -partially | Law and regulations list the types of works and activities that require an EIA; States and Federal District can demand an EIA under certain conditions. |
Nicaragua | X | – | Law lists types of projects that require an EIA. |
Panama | X | Law and regulations list the types of activities depending on the risks associated with the project. |
Source: Tiffer-Sotomayor et al., 2015
How is a screening conducted?
ExamplesTo determine whether or not the project requires an EIA, project proponents assess their project based upon a set of criteria determined by a designated agency.
To determine whether or not the project requires an EIA, project proponents assess their project based upon a set of criteria determined by a designated agency. It is important that screening be done as early as possible in the development of the proposal in order for the proponent and other stakeholders to be aware of possible EIA obligations. It is also important that screening be applied systematically and consistently, so that the same decision would be reached if others did the screening.
The European Union suggests a set of questions to quickly assess project proposals. These questions are designed so that a “Yes” answer will generally point toward the need for EIA and a “No” answer to one not being required (European Commission, 2001).
- Will there be a large change in environmental conditions?
- Will new features be out-of-scale with the existing environment?
- Will the effect be unusual in the area or particularly complex?
- Will the effect extend over a large area?
- Will there be any potential for transboundary impact?
- Will many people be affected?
- Will many receptors of other types (fauna and flora, businesses, facilities) be affected?
- Will valuable or scarce features or resources be affected?
- Is there a risk that environmental standards will be breached?
- Is there a risk that protected sites, areas, features will be affected?
- Is there a high probability of the effect occurring?
- Will the effect continue for a long time?
- Will the effect be permanent rather than temporary?
- Will the impact be continuous rather than intermittent?
- If it is intermittent will it be frequent rather than rare?
- Will the impact be irreversible?
- Will it be difficult to avoid, or reduce or repair or compensate for the effect?
In Honduras, Article 24 of Decree 189-2009 establishes that all projects, construction work or activities (both public and private) need to go through the a formal screening process prior to beginning construction and operation. Projects are screened according to four different categories (1, 2, 3, and 4):
- Category 1: Low-Impact Potential environmental or Low Environmental Risk.
- Category 2: Moderate – Low Potential Environmental Impact and Environmental Risk.
- Category 3: Moderate – High Potential Environmental Impact and Environmental Risk.
- Category 4: High Environmental Impact or Environmental Risk.
The screening process in Honduras is currently done using two forms: SINEIA F-01 and F-02 set up within the SINEACP Online EIA system. The first it is for low-impact projects (Category 1) and the second for moderate-impact projects (Categories 2 and 3). Low-impact or low-risk projects (Category 1) are not required to develop a full EIA. However, these projects still need to comply with existing environmental legislation and the Good Environmental Practice Code of Honduras (Article 30 of ED 189-2009). Exemptions are also provided to any activities identified in the regulation as not requiring an EIA (e.g., military or emergency activities). Project identified to be in categories 2 and 3 often require EIAs.
Megaprojects, defined as large-scale projects and those that are national in scope, are considered Category 4 and always require an EIA. Identifying an activity as a Category 4 megaproject is not done through the online system. It is the responsibility of the Secretariat of Natural Resources and Environment through the Directorate of Evaluation and Environmental Control.
Examples
More information on EIA and EMP regulations and procedures in general and in Honduras can be accessed here: Key Aspects of EIA Legislation and EMP.