By Dr. Kariuki Muigua, PhD (Leading Environmental Law Scholar, Policy Advisor, Natural Resources Lawyer and Dispute Resolution Expert from Kenya), Winner of Kenya’s ADR Practitioner of the Year 2021, ADR Publication of the Year 2021 and CIArb (Kenya) Lifetime Achievement Award 2021*
In several cases, Environmental Impact Assessment (EIA) license has been challenged on the basis that the it was issued before Strategic Environment Assessment as issued. One such case is the recently concluded National Environmental Tribunal (NET) Appeal in Greenbelt Movement & 5 others v National Environmental Management Authority & another; Kenya National Highways Authority (Interested Party), National Environmental Tribunal (NET) Appeal No. 19 of 2020 challenging NEMA approval of the Nairobi Expressway EIA. One of the issues the NET comprising Mohammed Balala (Chairperson), Christine Kipsang (Vice Chairperson), Dr. Kariuki Muigua, PhD (Member), Bahati Mwamuye (Member) and Waithaka Ngaruiya (Member) had to grapple with in making their landmark decision was whether the EIA was irregularly issued for lack of a strategic environmental assessment. The case has brought to the fore the question of when a Strategic Environmental Assessment is necessary whether on its own or as a prerequisite for Environmental Impact Assessment. In determining whether SEA is necessary, one has to look at the provisions of the Environmental Management and Coordination Act, No. 8 of 1999 and Environmental (Impact Assessment and Audit) Regulations, 2003 on SEA as well as the National Guidelines for Strategic Environmental Assessment (SEA) 2012 and case law.
The Environmental Management and Coordination Act in section 57A provides that “All Policies, Plans and Programmes for implementation shall be subject to Strategic Environmental Assessment.” The Act clarifies that for the avoidance of doubt, the plans, programmes and policies are those that are subject to preparation or adoption by an authority at regional, national, county or local level, or which are prepared by an authority for adoption through a legislative procedure by Parliament, Government or if regional, by agreements between the governments or regional authorities, as the case may be and determined by NEMA as likely to have significant effects on the environment. Further, all entities are required to undertake or cause to be undertaken the preparation of strategic environmental assessments at their own expense and submit such assessments to NEMA for approval in accordance with rules and guidelines prescribes by NEMA for in respect of Strategic Environmental Assessments.
Besides EMCA, Rule 42 of Environmental (Impact Assessment and Audit) Regulations, 2003 provides that: “(1) Lead agencies shall in consultation with the Authority subject all proposals for public policy, plans and programmes for environmental implementation to a strategic environmental assessment to determine which ones are the most environmentally friendly and cost effective when implemented individually or in combination with others. (2) The assessment carried out under this regulation shall consider the effect of implementation of alternative policy actions taking into consideration – (a) the use of natural resources; (b) the protection and conservation of biodiversity; (c) human settlement and cultural issues; (d) socio-economic factors; and (e) the protection, conservation of natural physical surroundings of scenic beauty as well as protection and conservation of built environment of historic or cultural significance. (3) The Government, and all the lead agencies shall in the development of sector or national policy, incorporate principles of strategic environmental assessment.”
The National Guidelines for Strategic Environmental Assessment (SEA) 2012 defines Strategic Environmental Assessment (SEA) as referring to “a range of analytical and participatory approaches that aims to integrate environmental consideration into policies, plans and programmes and evaluate the interlinkages with economic and social considerations. SEA is a family of approaches, which use a variety of tools, rather than a single, fixed and prescriptive approach. This process extends the aims and principles of EIA upstream in the decision-making process, beyond the project level and when major alternatives are still opens (UNEP, 2002). SEA represents a proactive approach to integrating environmental considerations into the higher levels of decision making, consistent with the principles outlined in Agenda 21.”
The principles of SEA include: (a) the sustainable use of natural resources, (b) the enhanced protection and conservation of biodiversity, (c) interlinkage of human settlement and cultural issues, (d) integration of socio-economic and environmental factors, (e) the protection and conservation of natural physical surroundings of scenic beauty as well as protection and conservation of built environment of historic or cultural significance, and (f) Public and stakeholder engagement. In turn, the benefits of SEA include safeguarding the environmental assets and opportunities upon which all people depend, particularly the poor, and so promote sustainable poverty reduction and development. SEA also helps in improving decision making related to policies, plans and programmes, in improving development outcomes and in strengthening and streamlining project specific EIA.
In order for the SEA process to be influential and to help improve policy-making, planning and decision-taking, it should: (a) Establish clear goals, objectives and targets of the PPP (b) Be integrated with existing policy and planning structures (c) Be flexible, iterative and customized to context (d) Analyze the potential effects and risks of the proposed PPP, and its alternatives, against a framework of sustainability objectives, principles and criteria (e) Provide explicit justification for the selection of preferred options and for the acceptance of significant trade-off (f) Identify environmental and other opportunities and constraints (g) Address the linkages and trade-offs between environmental, social and economic considerations. (h) Involve key stakeholders and encourage public involvement (i) Include an effective, preferably independent, quality assurance system (j) Be transparent throughout the process, and communicate the results (k) Be cost effective – avoid duplication of efforts and encourage synergies (l) Encourage formal reviews of the process after completion, and monitor PPP outputs and (m)Provide opportunities to build capacity for both its undertaking and use.
Screening is undertaken to determine the potential of a PPP to result in significant effects on the environment, hat is, to decide whether or not an SEA is required. Methods and techniques used to screen strategic proposals vary depending on the nature and the objectives of the PPPs, as well as the decision-makers needs. Screening could be influenced by amongst others, the sphere of decision –making involved (e.g. local, national or regional), whether a PPP is being developed or assessed, and the potential impacts associated with development in different sectors (for example water sector, housing sector, energy sector, etc) to which the PPP relate. Given that application of SEA can become a lengthy and expensive procedure if it is not appropriately focused, the SEA process needs to be carefully focused so that it looks only at the key strategic issues and take into account capacity constraints.
There are various methods available for screening, such as the use of formal “triggers” and checklists (that is, using a set of criteria or list of questions as prompts), seeking advice from a competent authority or other expertise, amongst others. These methods are used to indicate whether PPP is likely to have a significant environmental effect (both positive and negative) and a SEA should be carried out where significant effects on the environment are likely. In considering whether or not a SEA should be undertaken, it is necessary to take into account the nature of the strategic proposal and the nature of the environment that would be affected.
It is considered appropriate to carry out a SEA where, amongst others: the PPP is likely to result in significant environmental effects, taking into account the magnitude, duration and spatial extent of effects, the proposed PPP is likely to be politically or publicly contentious; the cumulative nature of the effects (i.e. the additive and synergistic effects) are likely to be significant; there are likely to be trans-boundary effects, that is, it is likely to affect other municipalities, counties, regions and countries). Further, SEA is needed where the level of confidence in predicting effects of the proposed PPP are low, there are inherent uncertainties and/or important gaps in information in predicting effects, and/or the PPP is unprecedented; risks to health, safety and/or the integrity of social or ecological systems are considered to be high; social and/or ecological systems have low resilience and high vulnerability to disturbance or impact (for example poor communities, sensitive ecosystems); and the existing levels of environmental quality are close to defined limits of acceptable change.
SEA is also considered appropriate where the PPP is likely to have a negative impact on unique, special or highly valued natural or cultural elements like threatened biodiversity, sacred areas and recognized local, county, national or international conservation or protection status, for example, nature reserve, heritage sites and Ramsar sites. SEA is also recommended where a PPP is likely to result in major changes in actions, behaviours or decisions by individuals, businesses, NGOs or government, that could lead to: the stimulation of development of infrastructure or other changes in urban or rural land use; an increase in the transformation and development of natural habitat or areas of nature conservation importance: major changes in the pattern of settlement, land occupation and/or demographics in an area: major changes in the development or use of technology, that could have negative implications for health and/or safety: the introduction of alien and potentially invasive organisms; changes in society’s consumption of energy and in particular fossil fuels, and therefore, in emissions of carbon dioxide and other greenhouse gases; and changes in the rate of society’s consumption of, and/or demand on natural resources, including water.
*This article is part of the series on Principles of Natural Resources Management in Kenya extracted from Legal Aspects of Strategic Environmental Assessment and Environmental Management by Dr. Kariuki Muigua, PhD, Kenya’s ADR Practitioner of the Year 2021 (Nairobi Legal Awards), ADR Publisher of the Year 2021 and ADR Lifetime Achievement Award 2021 (CIArb Kenya). Dr. Kariuki Muigua is a foremost Environmental Law and Natural Resources Lawyer and Scholar, Sustainable Development Advocate and Conflict Management Expert in Kenya. Dr. Kariuki Muigua is a Senior Lecturer of Environmental Law and Dispute resolution at the University of Nairobi School of Law and The Center for Advanced Studies in Environmental Law and Policy (CASELAP). He has published numerous books and articles on Environmental Law, Environmental Justice Conflict Management, Alternative Dispute Resolution and Sustainable Development. Dr. Muigua is also a Chartered Arbitrator, an Accredited Mediator, the Africa Trustee of the Chartered Institute of Arbitrators and the Managing Partner of Kariuki Muigua & Co. Advocates. Dr. Muigua is recognized as one of the leading lawyers and dispute resolution experts by the Chambers Global Guide 2022.
References
Environmental Management and Coordination Act, No. 8 of 1999;
Environmental (Impact Assessment and Audit) Regulations, 2003
Greenbelt Movement & 5 others v National Environmental Management Authority & another; Kenya National Highways Authority (Interested Party), National Environmental Tribunal (NET) Appeal No. 19 of 2020.
Muigua, K., Legal Aspects of Strategic Environmental Assessment and Environmental Management; Available at: http://kmco.co.ke/wp-content/uploads/2018/08/Legal-Aspects-of-SEA-and-Environmental-Management-3RD-December-2016.pdf (accessed on 23/02/2022).
National Guidelines for Strategic Environmental Assessment (SEA) 2012 and case law.