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Part III - Lessons Learned and Future Directions

Published online by Cambridge University Press:  06 February 2025

Damilola S. Olawuyi
Affiliation:
Hamad Bin Khalifa University, Doha, Qatar
Riyad Fakhri
Affiliation:
Hassan 1st University, Settat, Morocco
Type
Chapter
Creative Commons
Creative Common License - CCCreative Common License - BYCreative Common License - NC
This content is Open Access and distributed under the terms of the Creative Commons Attribution licence CC-BY-NC 4.0 https://creativecommons.org/cclicenses/

15 Integrating Biodiversity into Environmental Impact Assessments Lessons from the EIA Process in the Tigris and Euphrates Basin

Rozhgar A. Mahmood , Qaraman M. Hasan , and Damilola S. Olawuyi
15.1 Introduction

This chapter examines the important role of environmental impact assessments (EIAs) as tools for biodiversity and nature conservation in the Middle East and North Africa (MENA) region. Drawing on lessons from three major projects, concerns have been heightened about their biodiversity risks to the Tigris and Euphrates river basin, namely the Güneydoğu Anadolu Projesi (GAP) project in Turkey,Footnote 1 the Tropical Water Projects in Iran,Footnote 2 and drainage projects in Iraq.Footnote 3 The chapter discusses how project developers and planners can maximize the full value of EIAs to better anticipate and manage such biodiversity risks.

In practice, an EIA can be used to identify and minimize potential significant harm caused by water resource projects and industrial developments in relation to water quantity and quality measures. Conducting a transboundary EIA for water projects across borders is therefore a recognized procedural obligation of international customary law.Footnote 4 EIAs provide a framework for project planners and regulators to effectively anticipate and prevent transboundary harm associated with large-scale dams and other water projects. As discussed in Chapter 3, failure to address the adverse impact of development projects on water security could worsen biodiversity loss and the extinction of plants and animals that depend on wetlands and other natural habitats. Understanding the relationship between the EIA and protecting biodiversity, and when it becomes significant, is therefore determinative in defining the impacts one assesses when conducting EIAs.

Across the MENA region, all infrastructure development projects are legally required to undergo some form of EIA to receive governmental approval or regulatory permit.Footnote 5 However, as demonstrated in this chapter, the terms and scope of an EIA are largely open to interpretation. This ambiguity is compounded by uncertainty in reconciling the damage which could result from projects and the legal concept of harm to diversity, which proponents must guard against. Concerns have been raised relating to the reduction of water levels in the Tigris and Euphrates rivers as a result of large-scale dam projects undertaken since 1950, permanent changes to the wetland ecology of the region, and a lack of widespread engagement from stakeholders impacted by such projects, all of which raise the need for a more comprehensive implementation of EIA norms in the MENA region.Footnote 6 Furthermore, the implementation of EIA processes will need to be better monitored across the MENA region before and after the approvals of development activities, in order to ensure that approved activities are being implemented in accordance with approved environmental quality standards and technologies.Footnote 7 This is not exceptional, even in new mega-projects such as the Grand Ethiopian Renaissance Dam, which may cause floods in the Nile Delta in both Egypt and Sudan,Footnote 8 or in the GAP in Turkey, which has led to biodiversity loss, as discussed in Section 15.3.

While several studies have examined the importance of EIAs as an important anticipatory tool for halting biodiversity loss, the challenges hindering its effective implementation to address biodiversity risks in the MENA region has yet to be exhaustively analyzed. This chapter fills a gap in this regard. It draws salient lessons from how the lack of comprehensive EIAs in water projects on the Tigris and Euphrates river basin has had diverse and adverse consequences on the environment and biodiversity of the basin. It discusses how the EIA could be enhanced in current and future developments in the basin by improving legal frameworks at the national level, increasing institutional capability, and integrating technological advancement into the fabric of EIAs.

The chapter proceeds in five sections, this introduction being the first. Section 15.2 maps the interdependent relationship between EIAs and biodiversity protection, drawing from key international law instruments, including the Convention on Biological Diversity (CBD), the Convention on Environmental Impact Assessment in a Transboundary Context (Espoo) and International Court of Justice (ICJ) cases. This section demonstrates how the legal scope of the EIA is changing, based on a gradual evolution in international environmental law (IEL), particularly pertaining to biodiversity, to embrace a more comprehensive vision of biodiversity protection. Despite this positive change, biodiversity protection is still not sufficient in many countries in the MENA region. Section 15.3 examines the negative impacts of ignoring EIAs in the case of dams and projects on the Tigris and Euphrates river basins. The lack of a comprehensive EIA process has contributed to the considerable loss of biodiversity, as well as cultural and heritage values, in the wetlands south of Iraq. Section 15.4 discusses how gaps such as the lack of clear recognition of biodiversity in EIA legislation, inadequate stakeholder engagement, weak integration of human rights standards in assessments and planning processes, the lack of institutional coordination between water and environmental institutions, and resource and capacity constraints all weaken the EIA process for these projects. To address these gaps in EIA implementation in current development projects and other future development projects across the MENA region, Section 15.5 discusses the need for human rights impact assessments as part of a comprehensive planning process. Section 15.6 is the concluding section.

15.2 The EIA as a Tool for Biodiversity Protection and Nature Conservation

The need for EIAs arose out of growing global environmental awareness in the 1950s and 1960s, and the recognition that industrial and other development projects were producing undesirable consequences on the environment.Footnote 9 In 1989, the United Nations Environment Program (UNEP) called for the necessity of concluding an international agreement on biological diversity. Work began by a specialized team in 1989 to prepare the agreement. This team continued its work and was called the Intergovernmental Negotiating Committee. It announced its adoption of the text of the international agreement in 1989, at the Nairobi Conference, and it was later concluded.Footnote 10 The agreement was announced to be open for signature at the Earth Summit in Rio de Janeiro on June 1992, and it entered into force on December 1993. One hundred ninety-three parties joined it. The goal of the agreement was “[p]romoting practices that lead to a sustainable future.”Footnote 11

In its preamble, the convention expressed its awareness of the fundamental value of biological diversity and ecological values, expressed its concern about the serious discrepancy in biological diversity due to human activities, and stressed at the same time that the basic condition for the conservation of biological diversity is the maintenance of ecosystems and habitats. The general objectives of the agreement, as stated in Article (1), is to ensure the conservation of biological diversity, the sustainable use of its components, and the fair and equitable sharing of the benefits arising out of the utilization of genetic resources.Footnote 12

For worldwide biodiversity, the most significant overall initiative is the CBD from 1992; the arrangement and the convention period put the focus on what biodiversity is, what it means to mankind, and what the globe will resemble for our children if we fail in safeguarding biodiversity at all its levels.Footnote 13 Here, the importance of the EIA is raised as a critical tool for the careful decision-making for the sustainable management of our resources, for considering best practices for protecting biodiversity in the long term, and for the care for the wider range of biodiversity beyond national borders. Article 14 of the CBD requires parties to mandate EIAs for their proposed projects that are likely to have significant adverse effects on biological diversity with a view to avoiding or minimizing such effects and, where appropriate, allow for public participation in such procedures.Footnote 14 It also requires parties to introduce appropriate arrangements to ensure that the environmental consequences of programs, activities, and policies that are likely to have significant adverse impacts on biological diversity are duly taken into account.

Conducting a transparent EIA in accordance with the CBD is a preeminent issue for international rivers or transboundary rivers because water projects and changing water flows from upper-stream countries to downstream countries will have an impact on the biodiversity of river basins. The CBD confirmed countries have permanent sovereignty over natural resources inside their boundaries, but they are responsible for not causing damage to the environment beyond their territories.Footnote 15 This is known as the do-no-harm principle in the IEL, which directly relates to the EIA and protecting biodiversity.

15.2.1 The Do-No-Harm Principle and the EIA: Protecting Biodiversity

The do-no-harm principle – avoiding or minimizing environmental harm – has been expressed differently, but the meaning is the same. We use do-no-harm as the abbreviation for all the earlier terms. It is considered one of the most significant principles for the international IEL.Footnote 16 It is one of the four essential principles of IEL with regard to the management of transboundary rivers.Footnote 17 According to the do-no-harm principle, states in transboundary river basins have a right to utilize the rivers. Still, they have a responsibility not to damage the environment of other states. It is usually linked to an equitable and reasonable allocation of transboundary rivers.Footnote 18 However, the overallocation of the rivers, in many cases, leads to damage to the environment of other states and biodiversity loss.

The do-no-harm principle has had a strong position since the twentieth century and at the early stages of the evolution of the IEL. The Madrid Declaration in 1911 insisted that changing the course of water, which leads to harm or putting waste into the water, is forbidden, as mentioned in Article 2.Footnote 19 In the Corfu channel case, the ICJ mentioned that states are responsible for damages to other states due to activities inside their territory.Footnote 20 Thus, the do-no-harm principle developed in customary international law until the UN Convention on the Law of the Non-navigational Uses of International Watercourses (Watercourses Convention) was formally recognized in 1997. Article 7 of the Watercourses Convention mentions that states are responsible for taking all necessary measures to avoid damage to other states during all stages of utilizing international watercourses.Footnote 21

According to the Watercourses Convention, the EIA is one of the most significant measures and tools for avoiding harm to other states. Article 12 of the Watercourses Convention clearly identified the EIA as a precautionary measure to prevent harm to transboundary rivers as the article refers to notifying other states and sharing information prior to planning projects, “including the results of any environmental impact assessment, in order to enable the notified States to evaluate the possible effects of the planned measures.”Footnote 22 This means states should conduct the EIA at the early stages of planning and designing projects, then share the results of the EIA with riparians to avoid harm, or take precautions, which is an effective method for communication and communication.

Similar requirements were raised in the Convention on the Protection and Use of Transboundary Watercourses and International Lakes (Water Convention), but with fewer details and in weaker language compared to the Watercourses Convention in 1977. The Water Convention encourages parties to apply the EIA “as far as possible” to reduce the negative impacts on other states.Footnote 23 However, the CBD more comprehensively linked the do-no-harm principle and the EIA to protect biodiversity beyond the national border. In addition to the provisions of Article 14 of the CBD, which introduces the EIA as a requirement for all projects that may have a negative impact on biodiversity, public engagement is also recommended in the EIA process.Footnote 24

As well as these important conventions, the Convention on Environmental Impact Assessment in a Transboundary Context (Espoo Convention) provided sufficient details regarding the procedure and practice of an EIA to achieve a better level of sustainable management of our natural resources. The Espoo Convention’s Article 1(vi) defined the EIA as a “means a national procedure for evaluating the likely impact of a proposed activity on the environment.”Footnote 25 Under the Espoo Convention, parties are responsible for undertaking the EIA “prior to a decision to authorize or undertake a proposed activity.”Footnote 26 This national procedure is a critical precautionary step for avoiding harm at the national and transboundary levels and protecting biodiversity. It would also result in the proper implementation of the do-no-harm principle. However, as Section 15.3 demonstrates, the lack of comprehensive implementation of the EIA process remains a key challenge in the MENA region. This is despite the fact that the countries of the MENA region are part of several regional environmental conventions that bind them to apply the EIA in designing their projects.

15.3 Mega-projects without Comprehensive EIAs on the Tigris and Euphrates Rivers

Despite the clear recognition of the importance of EIAs in regional and national instruments in the MENA region, the tendency of several development projects, especially large-scale dam projects with adverse impacts on biodiversity, to bypass the EIA process remains a key challenge.Footnote 27 This is evident in the Tigris and Euphrates basins. Turkey, Iran, Syria, and Iraq are the main riparian countries within the basin. Each of them continually works to guarantee that they have access to the necessary water supplies to suit their household, agricultural, and industrial needs.Footnote 28 In the absence of inclusive agreements and collaboration for the equitable sharing of water resources, riparian countries took unilateral steps and implemented projects that caused the reduction of the water quality of the entire basin and worsened its local and agricultural benefits with an adverse impact on biodiversity.Footnote 29

As dam construction permits exert control over large amounts of water, the riparian state can dictate flows and water availability in downstream countries. In the last fifty years, upstream countries on the Tigris and Euphrates have competed and built major dams on the two rivers and their tributaries without including EIAs and local people in the decision-making process.Footnote 30 Empirical studies have demonstrated that Turkey’s and Iran’s water projects have significantly reduced water quality and quantity in Iraq at surface and groundwater levels.Footnote 31 These projects are exacerbating climate change consequences for the two rivers.Footnote 32

The main issue in the basin is that all countries, but mainly the upstream states, have constructed many dams, and large-scale irrigation and hydropower projects, without proper consultation and communication with each other.Footnote 33 These dams have been built without an assessment of their impact on the environment. Most significant is Turkey’s extensive damming of the Euphrates, which has caused a drastic reduction of the water quality as a result of the decrease in the amount of water entering downstream territories. The water reduction due to these mega-dams contributed to biodiversity loss in Iraq; many species, including ferruginous duck, are under real threat.Footnote 34

In addition, decision-makers in the GAP project failed to apply international standards in constructing these dams and managing them. They largely ignored the EIA, resulting in the destruction of the cultural heritage of the Kurdish people, and the disregard for their cultural and environmental values. The GAP’s external credit companies claimed that they undertook the EIA but never shared it with the public.Footnote 35 Another crucial issue is that neither Turkey nor Iran have signed or ratified the Watercourses Convention.Footnote 36 This significant convention obliges states to share transboundary rivers equitably and avoid environmental damage to other states. The negative impacts of these dams are considerable on the lower part of the Tigris and Euphrates river basins or the marshlands and wetlands in the south of Iraq. The marshland is considered the birthplace of human civilization, with great environmental, cultural, and biodiversity values for Iraq and the world.Footnote 37

15.3.1 GAP: Development Projects or Destruction of Natural and Cultural Values

In the 1970s, Turkey started the damming project GAP, which was announced in the 1980s as a program to intensify the irrigation and hydroelectric capabilities of Turkey’s southeastern region. This project consists of a total of twenty-two dams (with a capacity of around 120 billion cubic meters). It contains nineteen hydroelectric electricity-generating stations across the Tigris–Euphrates basin, which were expected to be completed by 2010 but which has been extended to the end of this decade, approximately 73 percent of which have been finished, and several irrigation projects.Footnote 38

Mesopotamia, the land between the two rivers, was known as the most ancient productive farming area in the history of humanity. The Tigris and Euphrates played a major role in creating and developing the Sumerian, Babylonian, and Assyrian civilizations.Footnote 39 The GAP project grants Turkey the hegemony to monopolize the water of the Tigris and Euphrates rivers. This hegemony has already had an impact on agricultural production in the area and the livelihoods of millions of people who depend on it, whether for agriculture or as a primary source for everyday use for drinking and household needs.Footnote 40 The completed GAP projects have already made life difficult in the downstream countries, and if the damming continues according to the current trend, the adverse effects of diversity loss in the region will be grave.

Since the beginning of the GAP in 1989, the water salinity of the Euphrates has started to increase rapidly, which is predicted to increase drastically as the GAP approaches full development.Footnote 41 This constant decrease in the water quality in the downstream basins will make Iraq unable to reclaim its previous rich agricultural soils effectively.Footnote 42 Additionally, it would halt the naturally occurring discharge of salt and other contaminants from the Euphrates–Tigris system, whose soils are generally heavy and have drainage issues, making them unsuitable for agricultural use.Footnote 43 The daily functioning of the power plant will produce water surges downstream of the dam, which will harm the ecology below.

The downstream countries’ human and animal health will be further complicated by these variables, which will severely degrade the river environment and make it difficult for many species to survive.Footnote 44 The Tigris basin is renowned for its vast biological diversity, despite the fact that many parts of it have never been subjected to biological surveys. Mesopotamia is also the birthplace of numerous plants and agriculture.Footnote 45 Its extensive, intact river environment, which is home to numerous endangered animal and plant species, a significant portion of the Tigris, and its tributaries will be impacted by the upstream GAP. Agriculture, fisheries, and aquaculture have all experienced significant decreases as a result of declining river flows and deteriorating water quality in the basin.Footnote 46

15.3.2 The Tropical Water Project in Iran

Iranian development projects on the tributaries of the Tigris have negatively impacted the water quality and quantity of these tributaries since several of them rise in Iran, and as far as Shat Al-Arab is concerned, Iran and Iraq are the two primary riparian nations. Iran currently diverts the Tigris River’s tributaries through the Tropical Water Project, which is made up of numerous dams and tunnels, before crossing the boundaries of Iraq.Footnote 47 According to a Food and Agriculture Organization assessment, Iran began construction of a sizable dam on the Tigris’ tributaries in 2004.Footnote 48

The construction of the Daryan dam on the Sirwan River and the Sardasht dam on the Lesser Zab River, both of which flow into the Kurdistan region of Iraq, are the two most recent examples of aggressive dam building along the tributaries of the Tigris River in western Iran. In Khuzestan province, on the Iraqi border farther south, Iran constructed a massive embankment dam, essentially dividing the Hawiza Marshes.Footnote 49 Major portions of these wetlands have been completely parched on the Iranian side as a result of the dam construction along the rivers flowing to the Hawiza Marshes, resulting in the dust.Footnote 50

Similar to Turkey, Iran, as an upstream country, has started dam building without assessing its impact on the environment and has failed to apply international standards in constructing these dams and managing them by ignoring the EIA. Here, the negative impacts on Iraq are considerable on the marshlands that are home to rich biodiversity, most of which has been lost due to the drying up of the marshes.

15.3.3 Previous Iraqi Regimes and Drying up the Marshes

As well as the negative impacts on dams and water projects in the upstream countries, the previous Iraqi regime deliberately dried up large areas of the marshes in the south of Iraq.Footnote 51 The marshlands of Iraq were considered one of the largest wetlands in the Middle East, and one of the ten most important environmental areas on earth, according to UNESCO.Footnote 52 The Ahwar supports several criteria related to biodiversity which qualify them to be wetlands of high global importance.Footnote 53 These marshes are fed by the branches of the Tigris and Euphrates rivers, in addition to rainfed waters during the winter season and its consequent flooding period.

A portion of the Iran–Iraq boundary passes across the wetlands, and both countries built causeways and drained marshy sections during the 1980s war to improve access to the front. The Iraqi government began draining the remaining marshes following the first Gulf War and the Shiite Muslim revolt in the south, both of which were unsuccessful, to replace the marsh culture of fishing and rice farming with dry agriculture in order to eliminate the potential of rebellion.Footnote 54 To accomplish this goal, the central government began implementing five significant drainage projects to prevent water from the Tigris and Euphrates rivers from reaching the marshes. The region had been heavily polluted by poison gas and army ammunition. As a result, less than 10 percent of the marshes received water supplies by 2000 compared to two-thirds in 1993. Thus, most marsh dwellers were forced to leave their homes, and certain species and flora were gone.Footnote 55 The government at the time conducted numerous agricultural projects in the marshlands’ dried-out parts to alter the ecology.

Many villages and the plants and animals that lived there were burned when the project was finished. The water was poisoned to kill off all the fish and other aquatic life. The people’s primary source of food and money, the rice fields, were also damaged. Due to this operation, 500,000 marshland residents moved to other Iraqi cities or sought asylum in other nations. As a result, the marshes have turned saline and are unusable for farming due to frequent sandstorms.Footnote 56 After the fall of the Saddam regime in 2003, the Iraqi government, with the help of other countries and international organizations, started restoring and rehabilitating the Iraqi marshes.Footnote 57 The Ahwar of southern Iraq are located in an arid climate; these wetlands are home to a variety of biologically significant ecosystems, including those that support vulnerable species with major conservation and research value. It is one of the most significant freshwater ecosystems in the world.Footnote 58

Because they are major wetlands for the area and the world and our only remaining connection to the ancient Mesopotamian civilizations of the Sumerians, Babylonians, and Assyrians, the destruction of the Mesopotamian marshlands is one of the biggest humanitarian and environmental challenges facing Iraq.Footnote 59 It requires both an immediate and long-term planning response in order to restore the marshlands sustainably.Footnote 60 It should be regarded as the top environmental priority in Iraq, requiring a management strategy and significant assistance from international donor nations, international organizations, and nongovernmental organizations (NGOs).

15.3.4 The Negative Impacts of Dam Building on a Downstream Country (Iraq)

Dam building and operation have serious negative effects on the environment and society. In Syria and Iraq, people began to settle along the middle and downstream lengths of the Euphrates and Tigris around 6,000 years ago, which prompted the development of irrigation systems there. The two rivers originate in upper Mesopotamia, where there is abundant precipitation, then flow into central and lower Mesopotamia, where there is little precipitation and insufficient moisture for agriculture.Footnote 61 The Tigris and Euphrates rivers and their tributaries provide almost all of the water needed for domestic, industrial, and agricultural purposes.

Access to water in Iraq is significantly impacted by river diversions or flow decreases brought on by dam construction in Turkey and Iran.Footnote 62 People in Iraq and northeastern Syria suffer as a result of the GAP’s construction, as back-water irrigation is directed into the main channel in its upstream reaches, resulting in a decrease in water quantity and quality.Footnote 63 As a result of damming, numerous archaeological sites have already been inundated, but the number of primarily threatened archaeological sites is still unknown because of insufficient assessments of the river valley.Footnote 64

Another issue Iraq is dealing with is salinity. The upstream nations in the Euphrates and Tigris basin are seen to be the main contributors to Iraq’s declining water quality by damming and implementing irrigation projects, which slowly raise the water’s salinity while reducing its flow.Footnote 65 Farmers and fishermen have been adversely affected by salinity, particularly in southern Iraq, where many fish species cannot live due to the salinization of the water.Footnote 66 As a result of the farm and agricultural land reduction, intensive dust storms have taken place, climatic changes have been noticed, and higher temperatures are to be expected, and as a consequence regional environmental effects will appear.Footnote 67

As well as surface water, groundwater suffers from serious issues. It is expected that groundwater levels will drop further due to the reduction of infiltrated water from the rivers. This will have tremendous effects on the electricity supply and will have severe consequences on irrigation and industrial projects.Footnote 68 Further, it is likely that the electricity demands will be covered by the use of oil-heated power plants, thus increasing the emission of greenhouse gases such as carbon dioxide.Footnote 69

In addition, desertification is a major environmental and development problem in Iraq, which is caused by damming due to the decline of water flow of the Tigris and Euphrates rivers, the repeated frequency of drought, water quality degradation, and increasing soil salinity. As desertification leads to lower levels of organisms, it contributes to significant biodiversity loss compared to productive land. Large parts of Iraq have become deserts while it used to be productive farmland. Officials claim that in the last three decades, Iraq has lost most of its agricultural land, which has turned to desert.Footnote 70 The increase of desert areas caused frequent sand or dust storms, so the dusty days escalated from twenty-four days in the year between 1950 and 1990 to 200–220 days in a year in 2008–2009. This situation will deteriorate with the reduction of vegetation and palm trees due to the decrease of the Euphrates annual flow as a result of dam construction by Turkey.Footnote 71

Furthermore, the annual individual share of freshwater is another substantial environmental challenge. Iraqi officials and researchers claim that for a decade between 2009 and 2018, the individual share of fresh water has decreased dramatically, mainly due to the dam building by Turkey.Footnote 72 The drying of wetlands is another negative impact of dam construction by the upstream countries; due to filling the dams of the GAP, some of the Iraqi marshlands have lost about 55 percent of their area since the construction of the GAP.Footnote 73

In recent years, the Tigris and Euphrates rivers’ flow has taken on a significant amount of importance. In order to prevent further tensions in the Middle East, the growing demands for water by riparian nations would likely result in significant disputes in the near future so there is a need for more global attention.Footnote 74 These ecosystem services will continue to break down if the basin maintains its current pattern of poor management and in the absence of comprehensive agreements on resource sharing, which will result in enormous biodiversity losses to the region’s economies and to the livelihoods of the citizenry living within the basin.Footnote 75

15.4 Integrating Biodiversity into EIA: Legal Gaps and Responses

Although the majority of the papers and reports that are released by the United Nations water, environment, and agricultural organizations focus on the effects of drought, which is related to global climate change as a primary cause behind the catastrophic environmental problems and biodiversity loss in Iraq, it is not a coincidence that since the 1970s, the drought level has increased dramatically in Iraq, even without significant changes in the temperature and precipitation in the country. Overall, the upstream and downstream countries of the Euphrates and Tigris basins ignored and did not apply the EIA prior to building mega-dams on the two rivers, which is the main reason for the detrimental impact of water flow reduction and biodiversity loss. Many signs of biodiversity loss have been already observed in the basin, including loss of vegetation cover and agro-diversity, wildlife displacement, and ecological connectivity.Footnote 76 Long-standing environmental problems in the MENA region generally include (1) water shortage and quality, (2) land degradation and desertification, (3) coastline deterioration, and (4) urban and industrial pollution, which only vary in extent and severity between countries.Footnote 77

15.4.1 Legal Gaps: Legislation that was Never Fully Implemented

Weak regulatory and enforcement frameworks exacerbate these issues, which have a significant negative economic impact and environmental harm. In accordance with some of these nations’ existing environmental legislation, such as Article 2872 of the Republic of Turkey’s Environmental Law of 1983, the EIA should be considered before any mega-dam development.Footnote 78 However, the law does not provide a clear guide for actually implementing the EIA and how the EIA process should be enacted and executed outside Turkey. Additionally, according to the Environmental Protection and Enhancement Law of 1974, which designates the Department of Environment as the regulatory authority overseeing EIA, specific EIA requirements and procedures are established in Iran.Footnote 79 This law states that any action that could have a significant adverse effect on the environment may only be approved after an EIA has revealed its effects. It will look into the proposed measure’s geophysical, social, and cultural repercussions as well as its effects on flora, fauna, and habitats; transboundary effects are not included.

An analysis of domestic law reveals that the Euphrates–Tigris riparian states, particularly Turkey and Iran, used EIA as a local regulatory tool without considering the diverse effects outside their borders. Nevertheless, only Syrian law expressly requires the consideration of transboundary consequences. Article 14 of Decree 225/2008 addresses potential transboundary effects.Footnote 80 The extent to which the proposed policy’s transboundary effects must be considered by the competent authorities when determining whether or not it is environmentally acceptable and is still up for debate. How much the Syrian government takes into account transboundary implications while making decisions is unknown.

Federal Law 27/2009 is the main piece of environmental protection legislation in Iraq. Prior to the adoption of measures that are likely to have a major impact on the environment, an EIA must be undertaken, according to Article 10 of the legislation.Footnote 81 However, it does not mandate that transboundary effects be considered. Furthermore, Federal Law 27/2009’s provisions are still quite ambiguous, and federal legislators have not yet approved any follow-up regulations that would clarify EIA obligations or procedures and it does not provide sufficient detail on the various steps and issues involved in conducting the EIA process. Also, there is a lack of legal provision for strategic environmental assessment.

Furthermore, the countries bordering the Euphrates–Tigris river system are not signatories to any international agreements that would oblige them to carry out transboundary EIAs before deciding on a course of action that might have a significant impact on the Euphrates–Tigris river system. Additionally, regional agreements only cover particular geographic regions.

Overall, the bulk of developing countries’ failure to implement the EIA process successfully is attributed to a lack of competent implementation or political will, which is the primary cause of the EIA process failing in the MENA region, as it is in the majority of developing nations where there is still a wide gap between what is really done in practice and what is perceived to be true about EIAs despite significant improvements in law and policy. Although this is insufficient on its own to make the system functional, the fact that there are numerous regulations and an administrative framework may be considered one asset of the EIA system in Iraq and the MENA region. There are a number of defects and problems with the EIA system in the MENA region that are typically commensurate with flaws in many developing nations.

Wide-ranging challenges are encountered when implementing EIA in the MENA region. First is the lack of meaningful public involvement at all levels of the EIA process as well as ongoing environmental ignorance. Developers make an effort to avoid public input. For instance, the GAP case reports have found that those still resident in the reservoir area and those already displaced by conflict do not appear to have been consulted about the dam.Footnote 82 The same concerns have been raised about theTropical Water Project (TWP) WTP dam construction in Iran.Footnote 83

A second key challenge to implementing the EIA process effectively is the unavailability and inaccuracy of data defining environmental baseline conditions. Thus, decisions about effect evaluation are based more on personal judgment than on scientific research and prediction. As in the GAP dam construction reports found, due to security concerns in the area, it is doubtful that a comprehensive assessment of historic, cultural, or spiritual sites could occur in any of the reservoir regions.Footnote 84

Third is the lack of a national policy culture that encourages EIA implementation and application and acknowledges the dedication, administrative infrastructure, and methodological resources at the necessary levels.Footnote 85 A lack of clear and comprehensive national strategies on evaluating biodiversity risks in mega-projects often result in inconsistency in evaluating biodiversity risks in EIA reports which could have an impact on programs, plans, and policies.Footnote 86 Furthermore, in practice, the EIA screening and scoping are typically focused on the possible effects of a single proposed project, ignoring the cumulative environmental effects of multiple projects in the same area on biodiversity and nature conservation.Footnote 87 There is a need for clear and comprehensive guidelines on the nature and extent of specific biodiversity-related scoping and screening that should be done to identify, address, and prevent biodiversity and nature risks in mega-projects.

Fourth is the inadequacy of regulatory fines and sanctions relating to EIA infractions in the MENA region generally. For example, the lack of clear and comprehensive EIAs in the case of dam construction of the Euphrates–Tigris basin are mostly caused by a lack of harsh enough sanctions for noncompliance with EIA legislation and policies. Such inadequacy or nonenforcement of regulatory sanctions are often tied to political pressure, with research indicating the potential for governments in some countries to prioritize economic development over the environment.Footnote 88

15.5 Enhancing Biodiversity through Comprehensive EIAs

Dam construction under the GAP Plan, Tropical Water Project in Iran, and other projects in both Iraq and Syria should not be continued without undertaking EIAs to avoid further environmental issues and biodiversity loss. If they continue, they would cause political turmoil and misery for millions with considerable biodiversity loss in Syria and Iraq. Baghdad now has little influence over its neighbors in the region and scant resources to repair its deteriorating water systems in the post-ISIS environment due to years of turmoil and internal conflict. A comprehensive plan to address the nation’s environmental issues has not been developed due to weak IEL in the region. Currently, the Ministry of Water Resources is battling to reconcile the conflicting demands for water for irrigation, drinking, industry, and hydroelectricity while some of the nation’s hydrological infrastructure is still damaged by fighting or militant activity.

However, biodiversity protection in the ancient basin should not be less prioritized among riparians and proper implementation of all stages of the EIA is the first and crucial step to achieving most of the environmental goals in the region. It is suggested that these nations get through the challenges they are facing when using EIA because a successful and efficient implementation of the tool could be the answer for the Euphrates and Tigris basin countries.

To maximize the full value of EIA as a tool for advancing biodiversity and nature conservation, there is a need for comprehensive legislation that mandates the transparent conduct of EIAs prior to the approval or commencement of any mega-project with a potential impact on biodiversity. All development plans, programs, initiatives, and projects must be based on comprehensive EIAs that address all potential environmental and social risks, including risks to water bodies. EIA legislation, like other environmental regulations, should be precise about how enforcement is to take place and should be unambiguous about what constitutes effective penalties.

Second and related to this is the need for a national policy environment that encourages the use of EIAs and acknowledges the commitment, administrative and methodological infrastructure, and resources at the necessary levels. Such policies would elaborate the need for effective public engagement during the EIA process, as any EIA process is unlikely to be successful without productive engagement with potentially affected stakeholders. In addition to conducting targeted vulnerability assessments to determine potential risks to marginalized and at-risk groups such as women, youth, and indigenous groups, there is also a need to ensure that all pertinent points of view are taken into account throughout. The scoping and review phases of the EIA process need effective engagement with regulatory agencies, stakeholders, and the general public. Furthermore, NGOs, academic institutions, and organizations that are impacted must be adequately consulted and enabled to participate in EIA processes.

Third, after the necessary scoping on biodiversity risks, consideration of mitigation measures should be given to each impact individually and collectively. For example, in instances of heightened risks of biodiversity loss in marginalized communities and areas, there is a need for tailored programs to address such adverse impacts. Additionally, mitigation must take into account the role of technologies to gather data on biodiversity risks and to monitor the implementation of mitigation measures.Footnote 89 Digital technologies, “such as Environmental Systems Research Institute (ESRI) StoryMaps, purpose-built web-solutions and bespoke-built websites,”Footnote 90 can also ensure that EIA reports are produced and disseminated in a manner that is accessible to the general public, through the use of local languages and reporting approaches that aid public awareness and knowledge.

Fourth is the need for improving capacity building on the design and implementation of EIA programs. As awareness on environmental law increases across the MENA region, there is a need to ensure tailored education programs on biodiversity conservation and management with a focus on environmental planning through EIAs.Footnote 91 Critical to promoting awareness on EIAs is the need for MENA universities to ensure the teaching of environmental law-related courses as core courses in bachelors, masters, juris doctor and doctoral research programs. Furthermore, there is a need for executive certificates and courses on EIA design and implementation in order to promote practical knowledge and best practices on EIA reporting, EIA data collection and dissemination using digital technologies, and avoiding social exclusions in the design and implementation of EIAs. Such certificate programs can enhance continuous professional development and in-house training, thereby increasing the number of EIA professionals, as well as on promoting environmental awareness needed to avoid biodiversity risks in mega-projects.

15.6 Conclusion

Despite prevailing ambiguities and uncertainties in the legal enforcement mechanisms, EIAs remain important tools for averting and addressing biodiversity risks relating to mega-projects, especially infrastructure developments such as the GAP project in Turkey, the Tropical Water Project in Iran, and drainage projects in Iraq that have adverse impacts on the biodiversity of river basins. The transboundary environmental issues raised by these projects have the potential to destabilize an already tense region further. Compliance with the requirements of international biodiversity law and policy with regard to EIAs and environmental planning can serve as a foundation for discussions, and policymakers should be aware of the ground rules well before the crisis develops further. An international agreement is urgently needed to handle the issue of distributing the Tigris and Euphrates rivers’ water supplies among the riparian nations fairly and equitably to avoid other interconnected environmental issues such as biodiversity loss.

Additionally, none of the riverine nations, especially the upstream hegemons, should be permitted to continue freely constructing huge dams and using the water from the two rivers without EIAs and in defiance of earlier IEL. No riparian state along the Euphrates–Tigris has publicly stated their stance on the need for a transboundary EIA. All riparian states should hold bilateral and multilateral negotiations on dam activities and integrating an EIA. When new projects are being planned or implemented, international development and financing entities helping with water infrastructure projects in the Euphrates–Tigris basin should ensure that environmental and impact evaluations are undertaken prior to the commencement of such infrastructure development activities.

16 Multistakeholder Participation in Biodiversity and Nature Conservation in the MENA Region

Funmilola Ayotunde
16.1 Introduction

This chapter analyzes the importance of involving diverse stakeholders in biodiversity management in the Middle East and North Africa (MENA) region and proposes the multistakeholder participation (MSP) approach as an integrated framework for achieving productive and sustainable stakeholder engagement in biodiversity and nature conservation. While the literature has extensively highlighted the benefits of involving a broad range of stakeholders in environmental decision-making, minimal attention has been devoted to the opportunities and challenges of applying multistakeholder approaches to biodiversity and nature conservation efforts in the MENA region. Applying the MSP as a normative tool, this chapter prescribes legal and institutional framework considerations for ensuring the valuable contributions of multiple participants and community-based programs in biodiversity and nature conservation in the MENA region.

The MENA region is one of the world’s most endowed in natural and biological resources.Footnote 1 However, the region’s hot and arid climatic conditions, including desertification, drought, land and ecosystem degradation, and loss of biodiversity, pose complex challenges for nature conservation.Footnote 2 Water scarcity and climate change impacts aggravate the rapid loss of the region’s rich biodiversity.Footnote 3 With the declining biodiversity and deteriorating socio-economic conditions of vulnerable groups in the MENA region, especially local communities, the urgent need for cohesive and concerted strategies for biodiversity and nature conservation readily comes to bear.

Although there have been recent legislative and policy developments in MENA countries and at the regional level to halt biodiversity loss, there is a pressing need to provide more opportunities for community-based participation and the broad-based engagement of diverse stakeholders to contribute to environmental policy development and the pragmatic realization of action plans. Such important stakeholders include civil society, academia, nongovernmental organizations, and other members of the public, especially noncitizens.Footnote 4 Public participation in developing and implementing nature-based solutions to biodiversity challenges brings about numerous benefits: access to diverse perspectives and local knowledge; improving public support and a sense of ownership and responsibility regarding conservation initiatives; opportunities for public education of the importance of biodiversity and citizen’s roles in conservation efforts; and enhanced compliance with conservation regulations. The public can contribute significantly to the long-term sustainability of the ecosystem and the success of conservation plans due to their vested interest in the success of the initiatives they collectively developed and executed.

Environmental management programs will also need to carefully respond to the needs of often marginalized groups such as women, children, low-income individuals and families, and those residing in coastal areas.Footnote 5 Often situated in coastal or rural regions, local communities are highly vulnerable to environmental shocks. They are especially susceptible to the impacts of biodiversity loss because of their heavy and direct reliance on biodiversity-dependent ecosystem services. Hence, the declining biodiversity affects their access to basic needs, fresh water, and food, causing a decrease in agricultural production and means of sustenance. Therefore, this chapter focuses on local communities as vulnerable groups bearing enormous and disproportionate burdens of biodiversity loss and groups with unique knowledge that could help reverse declining biodiversity.

Community-based conservation programs recognize the interconnection between nature and culture and seek to incorporate community traditions, values, knowledge, and socio-economic development into environmental conservation.Footnote 6 Such programs require the active participation of local institutions and give community members and institutions control over aspects of conservation plans that directly impact them. Community participation in biodiversity programs is essential to promote community environmental stewardship, long-term commitment to sustainable use of biodiversity components, and equitable sharing of conservation responsibilities, costs, and benefits.Footnote 7 Community-based conservation programs protect local communities’ rights and encourage partnerships between local communities and private and public agencies to preserve the ecosystem. They lead to social, economic, and ecological development, incentivize biodiversity and nature preservation, and lead to a healthier ecosystem.

Considering the widely acknowledged significance of community-based nature conservation, this chapter highlights the centrality of local communities in environmental regulation and the efficient implementation of nature conservation schemes. This chapter consists of five sections. Following this introduction, Section 16.2 provides the contextual overview and basis for the MSP approach to biodiversity and nature conservation. Section 16.3 analyzes the factors for effective and beneficial multiparty collaboration. Despite the identified benefits of MSP in environmental management, Section 16.4 discusses potential barriers to the proposed inclusive approach – in light of MENA countries’ subsisting top-down conservation regulatory systems and practices. Section 16.5 recommends strategies for addressing or circumventing the obstacles, and Section 16.6 provides a conclusion.

16.2 The Multistakeholder Approach to Biodiversity and Nature Conservation

The MSP approach to biodiversity and nature conservation involves the collaboration and engagement of diverse stakeholders in planning and executing conservation policies.Footnote 8 It is an inclusive strategy that seeks to garner diverse perspectives and contributions of people and institutions with stakes in a project or initiatives to achieve more comprehensive and sustainable outcomes. This approach is increasingly proposed by the UN, encouraging all its entities and states to promote dialogue between those with stakes in a given issue or decision.Footnote 9 The multistakeholder strategy is an offshoot of the human rights-based approach (HRBA) to development, a UN-led normative framework that situates recognition and respect for human rights at the core of every decision-making process.Footnote 10 The HRBA promotes human empowerment through rights awareness, access to remedies and institutional promotion, and protection of human rights. The human rights-based approach is underpinned by five principles: universality, indivisibility, equality and nondiscrimination, participation, and accountability.Footnote 11 Stakeholder participation in decision-making and project execution is one of the cardinal standards for mainstreaming human rights standards into public governance.

The MSP approach involves various stakeholders or interest groups in decision-making. The meaningful participation of social actors, such as local communities and vulnerable groups, is fundamental to attaining development goals,Footnote 12 hence the interrelationship between effective participation and development. In a broader sense, participation and human empowerment are foundational to the human rights approach to nature conservation. In this context, participation goes beyond an instrument for obtaining public acceptance of a policy; participation is a right that must be respected.Footnote 13 The key objective of stakeholder engagement is to enhance trust among different actors, share information and institutional knowledge, and generate solutions and relevant best practices.Footnote 14 For biodiversity and nature protection initiatives, the MSP approach can help catalyze more acceptable decisions and greater sustainability of the outcomes, and minimize technical, environmental, social, and financial risks.Footnote 15 The MSP framework is a shift from top-down strategies where government agencies, extractive corporations, and investors, far removed from the daily realities of local communities and the majority of the public, formulate policies and execute projects.

The engagement of diverse stakeholders in tackling complex environmental challenges and nature conservation has gained popularity in the literature,Footnote 16 and found expression in international law.Footnote 17 The Convention on Access to Information, Public Participation in Decision-Making and Access to Justice in Environmental Matters (Aarhus Convention)Footnote 18 and its Protocol on Pollutant Release and Transfer Registers (PRTRs)Footnote 19 provide the legal basis for procedural environmental rights. The preamble of the Aarhus Convention underscores the importance of access to information and public participation in decision-making, which includes improvements in the quality and execution of decisions, enhanced public awareness, providing avenues for the public to articulate their concerns, and the creation of opportunities for public authorities to address the public’s anxieties.Footnote 20 The Aarhus Convention obliges state parties to provide a mechanism for public participation and access to information in environmental decision-making.Footnote 21

Particularly, the UN Convention on Biological Diversity (CBD) aims to promote “the conservation of biological diversity, the sustainable use of its components and the fair and equitable sharing of the benefits arising out of the utilization of genetic resources.”Footnote 22 With the overarching aim of fostering actions to protect and sustainably use biodiversity for current and future generations, the CBD encourages state parties to extensively utilize local communities’ cultural practices and expertise applicable to biodiversity protection and sustainability.Footnote 23 State parties are also obliged to implement environmental impact assessment procedures and, where appropriate, give the public the opportunity to participate.Footnote 24 The first protocol to the CBD, the Cartagena Protocol on Biosafety to the Convention on Biological Diversity (Cartagena Protocol), requires state parties to promote and ensure public awareness and involvement in safely transporting, using, and handling living modified organisms relating to biodiversity conservation and sustainable use.Footnote 25

Other international instruments that promote the rights to participation and access to information in environmental matters include the UN Framework Convention on Climate Change (UNFCCC),Footnote 26 the Stockholm Convention on Persistent Organic Pollutants (SCPOP),Footnote 27 and the UN Convention to Combat Desertification in those Countries Experiencing Serious Drought and/or Desertification, Particularly in Africa (UNCCD).Footnote 28 The United Nations has repeatedly stressed the importance of inclusive participation in environment-related policies.Footnote 29 As demonstrated in this chapter, despite the long-standing recognition of the significant role of the public in environmental management and development,Footnote 30 environmental laws and policies in the MENA region are yet to fully reflect this ideal.

16.3 Elements of Effective Multistakeholder Participation

Participation is not a one-way information-sharing process but involves all parties influencing the decision-making process through information sharing, deliberations, transparency, and collective decision-making. Due to the diversity of participants with various priorities and aspirations, varying levels of influence, and economic and social disparities, the successful application of the MSP approach in environmental management depends on the level of institutional integration of the fundamental and interdependent components of the approach.

The first issue is stakeholders’ access to adequate information. Information is a requisite for stakeholders’ informed deliberation, and the quality of stakeholders’ participation is defined significantly by their access to accurate information. The UN Human Rights Committee, in the case of Toktakunov v Kyrgyzstan, explained that the right to access information is not restricted to journalists or media, but private individuals and public groups can also exercise the right on issues of legitimate public concern.Footnote 31 To implement democratic and inclusive frameworks and programs that foster transparency, accountability, and reliability, such as the MSP approach, states must periodically and “proactively make available clear, complete, timely, reliable and relevant public sector data and information that is free of cost, available in an open and nonproprietary machine-readable format, easy to find, understand, use and reuse, and disseminated.”Footnote 32 The Rio Declaration on Environment and Development: Application and Implementation affirms the importance of access to information for effective public participation in environmental issues.Footnote 33 It states that everyone “shall have appropriate access to information concerning the environment that is held by public authorities … and the opportunity to participate in decision-making processes. States shall facilitate and encourage public awareness and participation by making information widely available.”Footnote 34

The Aarhus Convention underscores the need to provide the public with prior information before participation.Footnote 35 Furthermore, recognizing the interconnection of access to information and public participation, the PRTRs’ objective is to enhance the public’s access to information in order to expedite public participation in environmental decision-making.Footnote 36 Drawing from international law instruments and jurisprudence on environmental rights, providing adequate information to the public is a prerequisite to effective participation in and the actualization of environmental rights. While there might be minimal restrictions to information sharing, they can only operate within legal boundaries, but stakeholders must receive adequate and prior notification to make informed decisions.

Prior notification is the first of many steps in MSP. It involves informing the public about a planned project or initiative, for example, the project’s environmental considerations, long-term implications, if known, impact on the host/local communities, and involved state agencies. Notification is a single-sided communication process in which the public is informed about a proposed initiative and receives the necessary data. Such notice and materials should be received well before deliberations to give stakeholders ample time to consult with their group members and experts and prepare for deliberations. Prior notice with adequate information prevents conflicts and is the first step in gaining community buy-in.

Second, there must be appropriate representation of identified stakeholders. The MSP approach is a unique democratic model “whose goals reach beyond multi-party representation. They give allocated seats to different groups rather than majority vote, and make room for extensive deliberation, giving voice to weaker or smaller interests.”Footnote 37 Environmental degradation and biodiversity loss affect everyone and have multijurisdictional implications. However, some groups are overly impacted compared to others due to aggravating conditions such as proximity to extractive projects, living in a coastal region, and living with disabilities. Therefore, while ecological challenges impact every citizen, the MSP approach seeks to acknowledge diverse interests and give those often neglected in decision-making the avenue to contribute to environmental conservation.

To have appropriate representation, individuals and groups with legitimate stakes in environmental issues should be identified without discrimination. Aside from those usually involved in environmental management, such as government departments, those directly impacted and highly vulnerable to environmental challenges, such as local communities, should be represented. Stakeholders must be allowed to choose their representatives without government or external interference. It is not enough to appoint someone with ties to a community or group but far removed from their daily realities. Representatives’ knowledge of communities’ lived experiences impacts the quality of their inputs during deliberations. Therefore, representatives must be members of and have ongoing connections with the group or community they represent. Elections from various interest groups and communities allows for broad representation and perspectives. For instance, while communal representatives can provide historical and practical insights, scientists can contribute technical and research-based data. It is not enough to have diverse participants; delegates’ expertise also matters.

Third, deliberative democracy is another essential component of the MSP approach, which involves making decision-making conditional on stakeholder deliberations. That is, decisions are made subject to voluntary, free, and fair consideration by all parties. Access to information, the weight accorded to participants’ decisions, and the possibility of further dialogue and reconsidering issues are preconditions of productive stakeholder deliberations.Footnote 38 Deliberative democracy promotes the recognition of and respect for each stakeholder’s views, giving equal weight to their opinions because they represent the uniqueness of each stakeholder and the group they represent.Footnote 39 Each stakeholder must be considered equal, and their views and values accorded unbiased consideration. Issues raised should be open to discussion and questions, with participants consciously working toward a resolution agreeable to all or a majority. Although not all stakeholders’ interests and opinions can be accepted or implemented, they must be duly considered. It may be difficult to achieve equality considering the financial and power imbalance between stakeholders, but institutions should consciously work toward ameliorating such barriers.

Fourth, conflict management mechanisms are essential in the MSP model and could define stakeholders’ trust in the process. Due to differing priorities, perspectives, and values, misunderstandings among stakeholders are common. Therefore, to inculcate inclusive practices, institutions must maintain an efficient strategy for mitigating conflicts, mediating differences, problem solving, and helping parties work together regardless of their differences. An effective and unbiased dispute resolution process can help address power imbalance among participants, promote fair deliberations, mitigate knotty and time-consuming fallouts, and facilitate stakeholder collaboration. If poorly managed or unresolved, disputes may stall deliberations or lead to the untimely dissolution of multiparty processes.

Fifth, transparency and accountability are fundamental aspects of the MSP approach. Information concealment, discrimination against some groups, and favoritism in deliberations are hindrances to effective stakeholder collaboration. Onderscheid defines transparency as “being open about points of view, opinions, assumptions and expectations; being open about relevant business interests; supplying all relevant parties with all relevant information.”Footnote 40 Processes shrouded in secrecy and bigotry cannot thrive as stakeholders will not trust the outcome, thereby defeating the whole essence of the process. Stakeholders are accountable not only to the government but also to one another, and the government is accountable to the public to implement environmental policies and ensure compliance by actors such as extractive corporations and foreign investors. States can foster transparency and accountability by creating a channel for communities to submit complaints to the government department responsible for addressing complaints regarding environmental conservation or related issues. Institutions must establish clear policies and guidelines to ensure stakeholders’ transparency and accountability, such as participants’ responsibility to divulge necessary information, prohibition of backroom politics, and periodic publication of stakeholder deliberation reports.

Lastly, the MSP model is open-ended and requires committed participants who are willing to dedicate time and resources to ensure successful outcomes, including through the long-lasting project-monitoring, evaluation, and reporting phase. This phase requires a planned-out procedure, known to all participants, specifying how they can track and report on the progress of collectively developed plans. To facilitate evidence-based monitoring, evaluation, and reporting in conservation management, a quorum of stakeholders must be empowered to call for follow-up dialogue at reasonable intervals, participate in data collection and assessment, articulate their grievances, and demand accountability from defaulters. This is only feasible if participants can access government officials and representatives of other groups who are responsive to the concerns of others. This level of commitment to MSP is necessary because other factors may come to light after the commencement of a conservation strategy, or new concerns may arise after the conclusion of the initial deliberation phase. More so, accountability is a continuous process and requires the dedication of all stakeholders. Regular and continuous dialogue and feedback between stakeholders will help to address budding conflicts, foster long-term stakeholder contributions, and help evaluate compliance with stated objectives.

Despite the proven benefits of multistakeholder engagement methodologies to ecosystem management, the MSP approach has pockets of weaknesses, but the benefits greatly outweigh the identified limitations. The MSP tends to extend the decision-making time frame due to the involvement of multiple stakeholders and a prolonged deliberation process to accommodate parties’ needs and contributions. The time commitment may discourage stakeholders, especially government agencies accustomed to working with few parties and making speedy decisions. Additionally, including diverse parties with varying perspectives and priorities may lead to a clog in the wheel of progress. Regardless, the comprehensive contributions from multiple parties, improved quality and practicality of decisions, and widespread stakeholder buy-in are incentives worth the additional time and effort.

16.4 Barriers to Mainstreaming the MSP Approach into Biodiversity and Nature Conservation in the MENA Region

Integrating MSP into the MENA region’s legal and institutional structures has inherent setbacks which may delay its successful implementation, but they do not render it inoperable. Addressing the barriers to effective multistakeholder participation is essential if the region is to maximize the full potential of community-driven conservation as a tool for halting biodiversity loss and promoting nature-based solutions in the region. The gaps discussed in this section are not exhaustive but are paramount and cannot be overlooked in successfully implementing the MSP approach in the MENA region’s biodiversity and nature conservation.

16.4.1 Lack of Comprehensive Recognition of Participation Rights in Regulatory and Policy Instruments

The lack of comprehensive legal recognition of participation rights in environmental and biodiversity conservation regulations and policies is one of the leading barriers to integrating MSP into biodiversity and nature conservation in the MENA region.Footnote 41 Across the region, stakeholder engagement is often in the form of formal representation of the public by representatives in the Shoora Council or parliaments.Footnote 42 Several MENA countries do not provide direct opportunities for civil society, nongovernmental organizations (NGOs), academia, and members of the public that may be affected by a project or activity to actively participate in conservation strategy planning or implementation. While significant national regulations and strategies seek to promote the sustainable use and conservation of biodiversity, regulators in the MENA region have yet to unlock spaces for broad participation of the general public as legal decision-makers in conservation programs.

MENA countries have intensified their efforts to combat environmental degradation and biodiversity loss by signing international biodiversity and conservation treaties. All the countries in the MENA region have ratified or acceded to the CBD and its first protocol, the Cartagena Protocol.Footnote 43 All but Iran, Iraq, and Libya have ratified the second protocol to the CBD, the Nagoya Protocol.Footnote 44 The adoption of international instruments aimed at promoting biodiversity conservation and ecological sustainability by several MENA countries is a step in the right direction. However, a few MENA countries have paid minimal attention to the participatory rights provisions in the instruments. For instance, the Kingdom of Bahrain’s National Report to the CBD highlights the country’s progress in implementing the National Biodiversity Strategy and Action Plan between 2011 and 2014. One of the identified achievements is the improvement of public participation in biodiversity conservation, but there is no indication of public involvement in developing or executing the action plan. The country boasts environmental clubs in schools and the involvement of local NGOs in awareness programs and national biodiversity commemoration day planning.Footnote 45 While these efforts are important in raising awareness, there remains a need for the more direct involvement of such key stakeholders in the design and implementation of biodiversity strategies and programs. Similarly, as a party to the CBD, Egypt revised its National Biodiversity Strategy and Action Plan (NBSAP) to align with the CBD Strategic Plan. While Egypt acknowledged that the lack of stakeholder participation impeded the actualization of the action plan in the past and committed to policy implementation through a participatory approach, the country’s biodiversity strategic goals did not include plans to involve diverse stakeholders in the action plan implementation.Footnote 46 Without clear and comprehensive frameworks to widen MSP in the implementation of the NBSAP, advancing community-driven conservation may remain stifled in the country.

Additionally, national legislative and policy developments have been launched to set the region on track for achieving the United Nations Sustainable Development Goal (SDG) 15 on conservation and the sustainable use of the aquatic and terrestrial ecosystems, reverse environmental degradation, and end biodiversity loss.Footnote 47 For instance, the United Arab Emirates (UAE) outlined National Development Priorities and Strategies for achieving the SDGs by 2030.Footnote 48 Although the plan recognizes the roles of stakeholders in implementing the SDGs, the identified stakeholders are limited.Footnote 49 The SDG 14 and 15 implementation report shows that the UAE initiated action plans to conserve biodiversity, but there is no mention of the public’s role in implementing SDG 14. For SDG 15, the report recognizes the importance of public awareness, but there is no avenue for citizens to participate in the conservation initiatives. Instead, the emphasis is on raising public awareness about conservation and illegal wildlife trade through workshops, campaigns, and environment day celebrations.Footnote 50 Iran also developed national targets and strategies to achieve the SDGs.Footnote 51 Although the action plan was reportedly developed with the involvement of multiple stakeholders,Footnote 52 only executives and experts from government ministries attended the Department of Environment meetings.Footnote 53 Despite including public participation in the strategic goals, the action plans focused on public awareness without delineating procedures for public engagements.

Although many of the biodiversity conservation- and environment-related international instruments have been integrated into MENA countries’ domestic laws, the regulations and strategic plans fail to recognize the participatory rights of citizens. The lack of a clear and practical process for public engagement in strategic planning and conservation activities creates a critical gap and hinders the sustainability and effectiveness of conservation strategies. For example, the UAE passed a federal law on biosafety of genetically modified organisms in 2020 to protect local genetic resources and biodiversity,Footnote 54 and a federal law on access to genetic resources in 2021, in accordance with the Nagoya Protocol. Qatar’s Environment Protection Law and Saudi Arabia’s Environmental Law have provisions for nature and biodiversity protection.Footnote 55 However, none of these laws specifically refer to the right to participate in decision-making on biodiversity or conservation efforts.

Notably, the domestic regulations reflect the top-down and command-and-control approach, seeking to deter actions causing biodiversity loss or ecological degradation through penalties.Footnote 56 National and regional policies and action plans do not sufficiently recognize the role of stakeholders and fail to create avenues for diverse stakeholders to participate in environmental preservation processes. This oversight hampers the inclusivity of biodiversity and nature conservation initiatives in the MENA region and the eventual actualization of the set goals.

16.4.2 Limited Institutional Coordination among Regulatory Agencies

Besides the regulatory and policy framework gaps, the lack of clear and functional institutional coordination among institutions with biodiversity, environmental, and human rights mandates is another critical challenge for integrating the MSP framework into the MENA region’s conservation efforts. The development of national targets and institutions on biodiversity and nature conservation is indicative of governments’ recognition of the region’s exacerbating environmental challenges and willingness to tackle these issues. However, it is impracticable for uncoordinated institutions to actualize the region’s environmental goals. Biodiversity loss disproportionately impacts those mostly dependent on ecosystem services, including the poor, local communities, and subsistence farmers.Footnote 57 Environmental planning and economic developments must consider the impacts of the depreciating biodiversity-dependent ecosystem services on disadvantaged social groups to avoid further marginalizing vulnerable communities or groups. Thus, biodiversity and nature conservation transcend the purview of environmental or agricultural institutions and implicate the protection of socio-economic rights.

While MENA countries have developed national and regional institutions to tackle the declining biodiversity and environmental degradation, there remains a significant disconnect between environmental and human rights agencies. The UAE’s Ministry of Climate Change and Environment is the federal agency responsible for environmental planning and development of programs on biosecurity and environmental sustainability.Footnote 58 The ministry is required to work with local environmental agencies without any mention of the human rights ministry. The Justice, Safety, and the Law Department’s web page is silent on environmental or bioconservation issues.Footnote 59 For Qatar, the Ministry of Environment and Climate Change is the “sole and main agency responsible for research, enforcement and implementation for all aspects of environmental protection and biodiversity conservation in the entire country.”Footnote 60 However, the tendency of ministries and agencies to act in silos remains a key challenge.Footnote 61 There remains a clear need to strengthen communication and coordination between environment ministries and other relevant agencies and ministries such as human rights, foreign affairs, energy, and agriculture, given the key roles they play in advancing nexus and integrated implementation of biodiversity and nature-based conservation.

The Conference of the Parties remarked that the objectives of the CBD cannot be achieved until consideration of biodiversity is integrated across sectors. While the focus has been on sectors directly related to biodiversity, such as forestry and agriculture, there is a need “to mainstream the conservation and sustainable use of biological resources across all sectors of the national economy, the society and the policymaking framework is a complex challenge at the heart of the Convention.”Footnote 62 Human rights protection is a fundamental aspect of environmental causes, and MENA countries risk exacerbating the poor socio-economic conditions of vulnerable groups and further marginalizing local communities if left out of environmental management and activities.

Conservation programs that exclude the public, especially local communities, may yield minimal conservation results but at the expense of vulnerable groups’ rights. Disregarding local institutions, “green grabbing,” and community displacements have been linked to conservation programs.Footnote 63 These human rights challenges may fester if local communities and other stakeholders are not involved in conservation initiatives. To ensure that stakeholders’ rights, especially their participatory rights, are recognized and respected in biodiversity and nature conservation programs, MENA countries need to reevaluate their national biodiversity strategies and action plans and create a comprehensive institutional synchronization between their environmental and human rights agencies.

16.4.3 Limited Institutional Platforms for Local Communities

The lack of institutional coordination for environmental conservation issues in local communities is a corollary of the limited recognition of participation rights in environmental regulations and policies. The establishment of organized community platforms for collaboration, information exchange, and the coordination of conservation strategies remains slow across the region.Footnote 64 Additionally, the lack of organized structures for intercommunal alliances hinders knowledge sharing, environmental awareness, and widespread support for conservation action plans.Footnote 65 To facilitate institutional coordination among local communities, government departments need to create a platform for communal deliberation and the collective implementation of set environmental preservation goals. As discussed earlier, regulators in the MENA region have yet to acknowledge citizens’ participation rights in conservation programs. Thus, there is no institutional structure to facilitate local communities’ collaboration with civil society organizations, private actors, and other stakeholders.

The actualization of MENA countries’ conservation targets relies significantly on their recognition of local communities as stakeholders. Although the CBD encourages states to apply local communities’ practices and expertise in biodiversity conservation,Footnote 66 failure to create institutionalized platforms for local communities’ participation in conservation planning remains a preventable limitation to the integration of MSP across the MENA region. Local communities experience various drawbacks, often worsened by limited engagement and support by national authorities. Due to their unique experiences and rich traditional knowledge, these groups can contribute greatly to sustainable conservation practices. They are at the forefront of reversing biodiversity loss and protecting nature, but their voices may remain unheard without institutional platforms and support.

16.4.4 Finance and Capacity Gaps

Limited access to the financing needed to develop and implement biodiversity and nature conservation programs remains a key barrier to eco-entrepreneurship and community-driven nature-based solutions in the region.Footnote 67 In 2020, the World Bank, for the second time, reported an upswing in the rate of extreme poverty in the MENA region.Footnote 68 A combination of environmental degradation impacts, armed conflicts, and the COVID-19 pandemic has had devastating effects on the region and worsened socio-economic inequalities.Footnote 69 The region’s biodiversity loss has affected local communities further due to low agricultural production, food and clean water scarcity, and other compounding factors. Local communities rely heavily on biodiversity-dependent ecosystem services, and declining biodiversity affects their access to financing and basic needs.

Socio-economic inequalities are a barrier to the effective mainstreaming of MSP in the MENA region because of power imbalances. Inequities among stakeholders and prejudice in MSP processes can create mistrust and time-wasting gridlocks in deliberations. Furthermore, as discussed in Chapter 17, community-driven conservation efforts in the MENA region remain stifled by a lack of capacity and training support. The abilities of stakeholders to design and implement nature-based solutions and conservation programs can be strengthened through conservation-focused accelerator and environmental education programs that promote eco-entrepreneurship.Footnote 70

16.5 Mainstreaming the MSP Approach into Biodiversity and Nature Conservation in the MENA Region: Recommendations

Holistic and functional legal and institutional frameworks are imperative to mainstreaming MSP, but the limitations discussed in Section 16.4 remain hindrances to the MENA region’s biodiversity and nature conservation goals. With the requisite normative and institutional structures, the MSP approach could ensure that local communities’ aspirations are heard and that stakeholders have coherent institutional platforms to share their distinctive experiences and contribute knowledge and resources to biodiversity and nature conservation. This section proposes recommendations for circumventing the barriers and strategies for integrating MSP and successfully preserving the region’s biodiversity and nature.

16.5.1 Recognition of Stakeholders’ Participation Rights in Biodiversity Conservation Regulations and Plans

The sustainable and productive involvement of diverse interest groups in environmental conservation hinges on national regulatory standards that recognize those individuals or organizations as stakeholders and create avenues for their participation in decision-making and project implementation. A crucial initial step in MSP processes is the identification of interested parties to engage. Which raises the question, who is a stakeholder?

There are varying, and sometimes contested, conceptualizations and applications of the term “stakeholder.”Footnote 71 Generally, stakeholders are those actively involved in decision-making and those directly (or highly likely to be) impacted by a project, initiative, or policy. Determination of who a stakeholder is depends on what constitutes a legitimate stake.Footnote 72 In relation to environmental management, stakeholders are “individuals and social groups relevant to the effective design and implementation of given objectives, mechanisms, policies and programmes.”Footnote 73 In biodiversity and nature conservation, stakeholders refer to individuals, groups, and entities that are interested in, affected by, involved in, or can influence conservation outcomes. Considering the varying and extensive implications of nature conservation, stakeholders can span local, national, regional, and international realms. At the national and regional levels, they include government agencies, civil societies, farmers, businesses, scientists, academics, youth groups, and local communities.Footnote 74 Stakeholders include a broader range of social actors. Local communities, as actors disproportionately impacted by biodiversity loss and repositories of traditional conservation knowledge, are stakeholders in biodiversity and nature conservation.

The MENA region stands to benefit from inclusive strategies but requires a commitment to inclusive environmental governance and conservation efforts. The United Nations Development Programme, through case study research in Arab states, highlighted the benefits of community-based conservation practices, including improved food security, community conservation awareness, knowledge of sustainable use of resources, capacity for early warning processes, and local community buy-in and ownership of ecological policies and adaptation plans.Footnote 75

The practical implementation of the MSP approach in MENA’s biodiversity and nature conservation will depend on the amendment of existing regulatory frameworks and policies to expunge barriers to stakeholders’ involvement and restrictive and discriminatory yardsticks for identifying stakeholders. MENA states’ national biodiversity strategies and action plans must be revised to recognize the participation rights of stakeholders, including local communities, acknowledge the essential roles of local communities, and create opportunities for their participation in conservation governance and implementation. National biodiversity conservation laws and other related environmental regulations must align with MSP principles by recognizing environmental stakeholders, including local communities, and their right to participate in conservation planning and activities, and by creating avenues for their involvement in environmental decision-making.

16.5.2 Institutional Coordination between Human Rights and Environmental Institutions

The objectives of legal and policy regimes on nature and biodiversity preservation can only materialize through viable and responsive organizational coordination. The CBD proposes national biodiversity strategies and action plans as the primary planning and implementation tool for achieving the convention’s objectives.Footnote 76 In the same vein, the Subsidiary Body on Implementation of the convention envisages national biodiversity strategies and action plans as implementation tools required to foster the integration of biodiversity “at all relevant levels within political, economic and social sectors.”Footnote 77 This implies that biodiversity cannot be addressed only by environmental agencies but also by integration into different public sectors with the objective of “taking biodiversity into the core agenda and objectives of their decision-making.”Footnote 78 Although multiple government institutions are responsible for environmental protection,Footnote 79 biodiversity conservation is usually within the precinct of specified environment ministries. For example, the UAE’s Ministry of Climate Change and Environment and Qatar’s Ministry of Environment and Climate Change are tasked with biodiversity conservation and other environmental matters. Furthermore, these ministries are not required to collaborate with human rights bodies. Even for ministries involved in environmental protection generally, there is often little or no alliance with the justice or human rights system.

This demonstrates a prevalent misconception that human rights protection is mutually exclusive of environmental protection. This gap in environmental laws and policies transcends MENA national and regional spheres. At the international level, the UN Special Rapporteur on Human Rights and the Environment decried the UN Post-2020 Global Biodiversity Framework for making no reference to human rights or requiring human rights due diligence in conservation planning.Footnote 80 The ongoing biodiversity crisis requires reconsidering what conservation really means and how conservation plans can be implemented in a rights-based manner. Likewise, the MENA region’s biodiversity and nature conservation regimes have a human rights blind spot that must be addressed urgently. Without a robust and sustainable organizational alliance between environmental and human rights institutions, MENA countries risk further infringing the rights of local communities and other vulnerable groups. A human rights-based approach to biodiversity and nature conservation is only possible with a comprehensive and coherent organizational setup to integrate the visions and programs of human rights and environment ministries. In addition to prioritizing human rights in biodiversity and nature conservation regulatory and policy frameworks, MENA countries need organizational restructuring to desegregate human rights and environmental institutions.

16.5.3 Institutional Platform for Local Communities

As regulatory frameworks are optimized to protect participation rights, local communities need institutional platforms to participate in conservation programs effectively. The importance of coherent and well-organized institutional frameworks for successful stakeholder inclusion in environmental management cannot be understated. The MSP approach gives local communities the avenue to participate and the corresponding responsibility to commit to conservation deliberations and activities. MENA’s diverse local communities lack well-structured institutional platforms to collaborate, disseminate information and interests, and share resources and knowledge as they combat biodiversity loss and nature degradation.

As Axner aptly states, “when you have many groups with different views, resources, and skills applying their intelligence and strength to solve a problem together, the results can be like the work of superheroes.”Footnote 81 The variety of local communities in MENA countries is not a limitation of the MSP approach but a much-needed intellectual diversity and richness in shared living experiences. By engaging in MSP processes, various communities and groups could learn how to form and maintain associations and develop the dexterity needed to manage group members. However, for efficient coordination and collaboration, local communities need well-structured institutions to synchronize their interests, disseminate information, and work toward their collective goals.

Local communities need an independent public department to enable collaboration with other communities and stakeholders. Respective communities could develop organizations for internal administration but need government support in building and maintaining an extensive intercommunal structure. The government can also support local institutions by providing management, negotiation, organizational development training, and financial resources to establish and run the organizations without government interference. Such well-coordinated institutional structures would ensure the adequate dissemination of information, recognition of every group’s interest, community planning, and attainment of collective objectives.

16.5.4 Enhancing Stakeholders’ Capacity

The compounding impacts of environmental challenges and socio-economic variables often create tremendous burdens and inequalities for local communities. The MENA region’s local communities have been significantly impacted by biodiversity decline, and their basic needs might distract them from contributing effectively to biodiversity and nature conservation. To foster community-based conservation programs, MENA states must meet the capacity needs of communities through fund allocations and technical assistance. Regional organizations, businesses, and civil organizations can also help alleviate the burdens of local communities’ participation in MSP conservation processes by providing financial support. Allocated funds and financial aid can cover the cost of developing and executing community-based conservation strategies, consultation with experts, implementing awareness projects, and progressing monitoring and assessment. In addition to financial support, MENA countries can demonstrate a strong commitment to stakeholder engagement in environmental conservation by implementing capacity-building initiatives tailored to the peculiarities of different local communities, including environmental education, cultural knowledge integration, and technological training.

Aside from capacity building for local communities, developing the capacity of other stakeholders, including civil societies, youth groups, women groups, scientists, academics, and private enterprises will improve their awareness, integration of sustainable practices, and ability to set goals and launch and execute biodiversity and nature conservation programs effectively. Various groups’ needs will differ, ranging from financial needs to technical support, tools, workshops, and knowledge of biodiversity and nature preservation. Some capacity needs, such as knowledge gaps and management skills, can be met through stakeholder collaboration. This further highlights the need for the MSP approach and institutional platform to facilitate stakeholders’ convergence, support, and collaboration. Having different groups with coherent structures represented in biodiversity and nature conservation management will improve the outcomes of the MENA region’s biodiversity conservation initiatives.

16.6 Conclusion

MENA countries have ratified or acceded to the CBD and other international instruments on biodiversity and nature preservation. There has also been progress across the region in terms of developing national strategies and policies to promote sustainable use and conservation of biodiversity and nature. While the growing pace of regulations, policies, and strategic action plans reflect MENA states’ political willingness to tackle biodiversity loss, there remains a pressing need to address gaps in community-driven biodiversity and nature-based solutions. Particularly, the lack of institutionalized frameworks for stakeholder engagement and participation in conservation has not fostered widespread MSP.

Meaningful stakeholder participation is fundamental to developing and achieving extensive compliance with conservation policies. It is therefore important to transform legal and institutional frameworks on biodiversity to accentuate MSP, while providing finance, education, knowledge sharing, and collaborative engagement opportunities for a wide range of actors. As the MENA region grapples with the compounding implications of biodiversity loss and threats to human health and means of sustenance, there is also a pressing need to adopt a human rights approach to conservation and enhance regional policy outcomes. The command-and-control or punitive approach to biodiversity management alone is not a realistic normative foundation for tackling the MENA region’s deteriorating biodiversity and the associated challenges.

The MSP approach can foster the involvement and commitment of diverse stakeholders to biodiversity and nature conservation in the MENA region. This approach offers several benefits, including diverse perspectives and expertise, better decisions, enhanced legitimacy and credibility of environmental policies, wider public buy-in and implementation of biodiversity conservation plans and policies, and greater awareness and comprehension of the implications of biodiversity loss and the need for preservation. As environmental conditions change over time, the MSP approach allows for adaptable strategies that can be modified and applied to evolving occurrences. By involving diverse stakeholders, MENA countries can improve public knowledge, acceptability, and compliance with conservation laws and promote the widespread sustainable use of biodiversity components and practices that address citizens’ environmental, social, and economic needs.

Social actors play a significant role in shaping the actualization of environmental protection policies, much more than state agencies recognize. To harness the contributions of diverse stakeholders in biodiversity and nature conservation, MENA states need a paradigm shift and profound evaluation and modification of the normative underpinnings of conservation-related laws, policies, and action plans to protect participation rights, form institutional alliances between environmental and human rights institutions, and provide the resources to facilitate effective stakeholder involvement in conservation planning and activities.

17 Strengthening the Implementation of Biodiversity Treaties through Environmental Law Education

Eghosa O. Ekhator
17.1 Introduction

This chapter argues that reliance on environmental law education can be one of the strategies to improve the implementation of biodiversity treaties in the Middle East and North Africa (MENA) region. Drawing lessons from emerging best practices on environmental law education across the region, this chapter examines the role of environmental law education in advancing biodiversity and nature conservation. It discusses legal and institutional gaps that hinder the profusion of environmental law education in the MENA region and the key reforms necessary to address such gaps.

Biodiversity is vital to humanity and its continued existence cuts across the rights and duties of states and their obligations pursuant to a plethora of international environmental agreements.Footnote 1 Notwithstanding the avalanche of international mechanisms promoting biodiversity protection, there has been a massive decrease in biodiversity resources in many parts of the world, including the MENA region.Footnote 2 For example, the habitat loss of indigenous species within the MENA region is rising at a striking rate due to natural and human causes.Footnote 3 The MENA region has rich and diverse ecosystems which are currently under threat.Footnote 4 The 2015 International Union for Conservation of Nature (IUCN) Red List states that thousands of species within the MENA region are under threat, arising from the decline in biodiversity sources.Footnote 5 Some of the factors impacting negatively on the biodiversity in MENA include desertification, droughts, climate change, and wildfires.Footnote 6

Hence, El Kassab argues that the decline or worsening of biodiversity in the region is connected “to human activities that result from government policies as well as lack of awareness of the importance of biodiversity and its role in achieving food security and the protection of natural resources.”Footnote 7 As a result, some countries in the MENA region are categorized as biodiversity hotspots and have “lost at least 70 percent of its primary native vegetation.”Footnote 8 For example, Morocco has suffered from worsening droughts and this has had negative impacts on biodiversity in the country.Footnote 9 This is said to exemplify the extent of the threats to biodiversity in the MENA region. The situation has been worsened by the negative impacts of climate change, which is “considered one of the key drivers of biodiversity loss – intensified effects on the region’s wildlife, plants and other species are expected to increase.”Footnote 10 Furthermore, notwithstanding its substantial energy resources, the adverse or arid geographical circumstances of the MENA region (e.g. it is one of the driest, most water-stressed, and most food insecure areas in the world) makes it enormously susceptible to several environmental difficulties.Footnote 11

Against this backdrop, halting the rapid loss of biodiversity is of paramount importance to the MENA region. There have been concerted moves by the international community and relevant stakeholders in developing measures or mechanisms to ensure the survival of biodiversity, including by promoting environmental awareness and education.Footnote 12 Environmental education is a process or means that enjoins individuals (including students) to explore environmental and allied issues, participate in problem solving, and take action to improve and protect the environment.Footnote 13 Environmental education initiatives play a major role in improving environmental awareness in societies. This becomes of utmost importance in societies or countries that are facing the burden of environmental injustices.Footnote 14 Higher education institutions in the MENA region “can play lead roles in promoting the SDGs [Sustainable Development Goals] through courses, training, and research programs that expose students to the various legal regimes governing human relationships with the environment.”Footnote 15 As the Association of Environmental Law Lecturers in Middle East and North African Universities (ASSELLMU) notes:

“[I]mplementing holistic and comprehensive ELE [Environmental Law Education] courses can enhance evidence-based policy-making, societal awareness, and local empowerment on environmental law and sustainability in the region, specifically on issues related to water, energy and food security, climate change, clean technology entrepreneurship and preservation of cultural heritage.”Footnote 16

This chapter argues that awareness and understanding of biodiversity issues should be embedded in the law curriculum via environmental law education within the MENA region. Environmental law education, which is a subset or subcategory of environmental education, “focuses on the study of the core principles of law relating to the protection of the environment.”Footnote 17 Environmental law education can be integrated or actualized via already existing environmental programs offered by universities or as part of the legal education curriculum in the MENA region. In many parts of the world, scholars and other relevant stakeholders have suggested that awareness of environmental sustainability issues and climate change should be mainstreamed or embedded in the legal curriculum of educational institutions (especially universities), and accordingly the MENA region should not be left out. The environment is an amalgamation of a wide-ranging and rich variety of biodiversity sources and therefore it should be protected.

This chapter examines challenges to environmental law education on biodiversity and nature conservation in the MENA region. It examines how law students and lawyers in the MENA region could be better equipped with the requisite knowledge of the legal framework on biodiversity. The chapter is divided into five sections including the introduction. Section 17.2 discusses the role of environmental education in promoting the utility of treaties on biodiversity. Section 17.3 discusses the evolution of environmental law education in the MENA region and the challenges to biodiversity legal education in the MENA region. Section 17.4 examines how those challenges can be addressed through law and policy responses. Section 17.5 is the concluding section.

17.2 The Role of Environmental Education in Promoting Environmental Awareness in MENA

Generally, education (whether in formal or informal settings) can provide the tools to enable individuals and societies to tackle the scourge of environmental crisis or degradation.Footnote 18 Education can have transformative impacts on how society and individuals treat or act toward their environment. This is evident in the rise of transnational litigation filed by civil society organizations against multinational corporations in different parts of the world. In some of these lawsuits, the knowledge and expertise of individuals (litigants) and organizations have had positive impacts on the business strategy and activities of multinational corporations.Footnote 19

Education is vital for the equitable and sustainable use or consumption of biodiversity sources, and it is “crucial for mainstreaming biodiversity.”Footnote 20 Thus, within the MENA region context, environmental education can be integral as one of the tools in tackling biodiversity-related negative impacts on society. Environmental education can be traced to the mid-eighteenth century when scholars and educators suggested that students should “study nature, not book.”Footnote 21 Thus, some scholars have suggested that the early inspiration for environmental education can be traced to the works of philosophers and scholars who wrote on the utility of nature and the environment in the eighteenth century.Footnote 22 However, the term “environmental education” is said to have been used first in 1948, and the activities of the various UN international conferences on the environment have given a fillip to the rise of environmental education initiatives at the domestic and international levels.Footnote 23 Also, the United Nations Environment Programme (UNEP) and the United Nations Educational, Scientific and Cultural Organization (UNESCO) have also played a massive role in the spread of environmental initiatives in different parts of the world.Footnote 24

At the international level, many instruments promote the use of environmental education and awareness. For example, SDG 4 focuses on “ensuring inclusive and quality education and promote lifelong opportunities for all” by 2030. Also, Target 4.7 of SDG 4 avers that “all learners acquire the knowledge and skills needed to promote sustainable development, including, among others, through education for sustainable development and sustainable lifestyles” by the year 2030.Footnote 25 Furthermore, the UNESCO Education for Sustainable Development (ESD) 2030 Framework recognizes ESD as an important core of quality education and an essential facilitator of the seventeen SDGs.Footnote 26 Also, Article 6 of the United Nations Framework Convention on Climate Change 1992 acknowledges the utility of environmental education in the plethora of efforts of countries in tackling the climate change crisis. Thus, there are moves at the international and national levels to promote environmental education at different levels of study in various parts of the world.

There are also laws and policies promoting environmental education and awareness within the MENA region. For example, the Sustainable Development Initiative in the Arab Region 2002 encourages all Arab countries to integrate environmental education at all educational levels, “with a view to raising a new generation whose members are aware and conscious of their responsibility for environmental protection.”Footnote 27 Similarly, Article 7 of Qatar’s Environmental Protection Law states that “all authorities responsible of education shall include environmental awareness subjects in all the educational stages.”Footnote 28 Also, the Qatar National Vision 2030 aims to promote the development of environmentally friendly citizenry that appreciates the preservation or conservation of its natural heritage and its neighbors.Footnote 29 Furthermore, the United Arab Emirates has developed its National Environmental Education and Awareness Strategy 2015–2021, whose main aim is to integrate or embed environmental education throughout all education stages.Footnote 30 Thus, laws and policies on environmental education are burgeoning within the MENA region. Arguably, this is not fully reflective of the whole region.Footnote 31 However, scholars aver that there is a growing consciousness in environmental awareness in the educational systems within the MENA region.Footnote 32

17.2.1 Evolution of Environmental Law Education

Environmental law is a fast-growing and distinct legal discipline in the MENA region.Footnote 33 Furthermore, environmental law education is emergent in different parts of the world (including the MENA region). Environmental law education is a subset or subcategory of environmental education, and its emphasis is on the study of the fundamental principles of law concerning the protection of the environment.Footnote 34 UNEP has also been at the forefront of developing the global or international rule of law and environmental law education in different parts of the world.Footnote 35 This has also helped in the promotion and deepening of environmental law education initiatives in several parts of the world. Furthermore, students on environmental law programs or courses are expected to be exposed to a plethora of legal frameworks regulating human interactions with environment. Environmental law is also premised on a plethora of values, strategies, theories, assumptions, and regulatory principles.Footnote 36 Environmental law education also accentuates the utility or relevance of practical skills and requirements on how relevant stakeholders, including lawyers, academics, law firms, and businesses, can forestall, avert, and “mitigate environmental lability in their operations, especially through corporate social responsibility, sustainability reporting, green supply chains and procurements, and strategic risk management.”Footnote 37

In the context of biodiversity and nature conservation, environmental law education should also expose students and relevant stakeholders to the various national and international legal regimes on biodiversity and nature conservation. Furthermore, environmental law education for biodiversity and nature conservation should also equip relevant stakeholders in society with the necessary tools, knowledge, and practical skills to tackle the scourge of rapid loss of biodiversity and protect nature conservation.

Furthermore, according to the Training Manual for the Train-the-Trainers (TTT) Program in Environmental Law for Higher Education Institutions in the MENA Region, the elements of environmental law education include:

  1. 1. Critical thinking taught to students through application of theory, law, and evidence to assess and draw conclusions.

  2. 2. Awareness and sensitivity to the challenges facing the environment, including gaps in law and governance structures.

  3. 3. Information and knowledge exchange on the local contexts, barriers, and motivations to improve or maintain environmental quality, including ethics, religious, and/ or cultural values.

  4. 4. The delivery of pedagogical skills to students to identify and help resolve environmental challenges, and the deployment of legal solutions innovatively.

  5. 5. Participation by students in activities that lead to the technical and legal resolution of environmental challenges.

  6. 6. Legal vocation training for students through various pedagogical approaches.

  7. 7. Development and application of suitable pedagogical approaches, depending on contexts of environmental law education.Footnote 38

In different parts of the world, there have been concerted moves to develop environmental law education or environmental law teaching as one of the tools to prepare law students and lawyers with the knowledge and expertise to deal with the myriad environmental crises afflicting different parts of the world. This takes on more prominence against the backdrop of the negative impacts of climate change occurring in different parts of the world. Hence, today’s law students and legal practitioners ought to be trained to deal with these issues.Footnote 39 Consequently, the overarching academic pedagogical consensus is that teaching on sustainability and environmental-related issues should be integrated into the core or compulsory law curriculum and not just solely located in environmental law programs or modules.Footnote 40

The last twenty years have seen an astronomical increase in environmental law education in different parts of the world.Footnote 41 However, in many parts of the world, environmental law education is not compulsory for law students or fully integrated into the legal education curriculum.Footnote 42 This is particularly important given the background of the current climate crisis, the impacts of which are particularly felt in the MENA region. Notwithstanding these impacts, scholars have argued there is lack of climate change awareness in the MENA region.Footnote 43 For example, Olawuyi argues that:

Despite the grim reality of climate change, the MENA region remains one of the least prepared regions facing it. Clear and comprehensive legal frameworks on climate change have not been so easily forthcoming in many parts of the region. Furthermore, climate change education is still at an alarming stage of infancy in the region.Footnote 44

Hence, many tertiary or higher education institutions within the MENA region have not integrated climate education into their curricula.Footnote 45 Hence, akin to many universities in different parts of the world, climate education is not integrated into the training requirements for law students and legal practitioners.Footnote 46 Arguably the MENA region is no different.

According to Fowler and others, environmental law education emerged in the 1970s as a key constituent of the undergraduate law curriculum in various countries in different parts of the world.Footnote 47 There has also been a massive rise in the development of environmental law at the postgraduate and graduate levels in different countries. However, in some parts of world, environmental law has no place in the legal education curriculum, hence some scholars have argued that environmental law is not part of mainstream legal education and thus only a marginal component.Footnote 48 In the UK, environmental law is not a core or compulsory component of the undergraduate legal education curriculum and some scholars have argued that few students take up the study of environmental law for various reasons, including lack of future career prospects in the field.Footnote 49 Thus, there is a rapid decline in the number of students studying environmental law in UK universities.Footnote 50 However, there have been various suggestions made by relevant stakeholders, including academics and legal associations, on how to improve the study of environmental law and the need for the explicit integration of environmental law into the university legal curriculum in the UK.Footnote 51 On the other hand, in the UK and many other parts of the world, law students (and legal academics) are clamoring for the inclusion of environmental law into the university legal education curriculum.Footnote 52

17.2.2 Environmental Law Education in the MENA Region

According to Kameri-Mbote, the director of the UNEP Law Division, “environmental law education systems are relatively at a nascent stage especially within the MENA region. Additionally, environmental law has conventionally not been taught as a core legal subject thus leading to fragmented approaches in its teaching.”Footnote 53 However, the last few years has seen a growing appetite for environmental law education in the MENA region.Footnote 54 There has been a massive rise in the number of universities offering environmental protection-related topics in their curriculum in the MENA region. For example, in the 2019 report of the Arab Forum for Environment and Development (AFED) on “Environmental Education for Sustainable Development in Arab Countries,” a survey of the fifty-seven highest-ranked universities in the Arab region was conducted.Footnote 55 This survey is said to be the foremost wide-ranging review of environmental law components in schools and university curricula in Arab countries, in view of recognizing the various lacunae and suggesting strategies to improve the role of education in promoting environmental protection and the implementation or enforcement of the SDGs in the region.Footnote 56 Some of the findings of the survey include that in the last decade, universities in Arab countries have seen a fast increase in programs or courses connected to the environment and sustainable development.Footnote 57 Also, the AFED report found that, in total, fifty-seven universities in the survey offered 221 degree courses or programs relating to environmental issues or topics.Footnote 58 However, the majority of the these programs are scientific and technical degrees, which appears to take prominence over law, education, policy, and economics programs.Footnote 59

However, there have been various initiatives that have been developed within the MENA region to assist relevant stakeholders, including environmental law lecturers and scholars, on how to embed environmental awareness and environmental education within their curricula or practices. An example is the Training Manual for the TTT Program in Environmental Law for Higher Education Institutions in the MENA Region, which was jointly organized by the UNEP and ASSELLMU.Footnote 60 ASSELLMU has been at the forefront of seeking to mitigate the gaps in the frameworks on environmental legal education within the MENA region.Footnote 61 The program also aims to enhance the pedagogy and the delivery of environmental law programs and courses within the MENA region.

Despite the rise in domestic and regional policies, mechanisms, and laws on the environment within the MENA region, it is contended that “environmental law education is still at an alarming stage of infancy in the region, especially when compared to many other regions.”Footnote 62 Furthermore, in many parts of the MENA region, there have not been deliberate moves to integrate biodiversity awareness into environmental education. For example, there is a need for more specific and tailored workshops and TTT programs on biodiversity in the MENA region to further promote the integration of biodiversity awareness into environmental legal curricula in the various universities and higher education institutions within the MENA region. Biodiversity within the MENA region is currently under serious threat, and this has become a major issue among governments and other relevant stakeholders in the region.Footnote 63 In many parts of the world, governments are developing mechanisms and legal frameworks (including ratifying relevant biodiversity treaties) to tackle the biodiversity threats, and the MENA region is not left out. Furthermore, one strategy is to “ensure that people are conscious of biodiversity conservation is through education.”Footnote 64 Hence, reliance on environmental law education can be one of the strategies to improve the implementation of biodiversity treaties within the MENA region.

Section 17.3 focuses on the barriers militating against the successful implementation of legal education as a tool to improve the implementation of biodiversity treaties within the MENA region.

17.3 Challenges to Biodiversity Legal Education as a Strategy for Enhancing the Implementation of Biodiversity Treaties in the MENA Region

There are various challenges affecting the successful integration of explicit biodiversity awareness and training into legal education within the MENA region. Some of these barriers or challenges include the marginality of environmental law in legal education in parts of the MENA region, a shortage of qualified environmental law scholars and lecturers, funding and resource constraints, and political crises.

17.3.1 Lack of Comprehensive Legislation on Biodiversity and Nature Conservation

In the MENA region, environmental law has arguably come to prominence and of age, and it is one of the strategies that is being used to tackle environmental challenges in the region. According to Olawuyi, all states in the region have developed primary legislation focused on environmental protection and secondary regulations focusing on various environmental issues such as wildlife, fisheries, biodiversity, and the protection of endangered species.Footnote 65 However, many MENA countries lack comprehensive laws relating to biodiversity and nature conservation. For example, according to the information available on the Convention on Biological Diversity (CBD) website, many countries in the MENA region have ratified the CBD, but they are yet to take concrete actions to implement or achieve the 2020 Aichi Biodiversity Targets.Footnote 66 Furthermore, regarding Jordan and its international biodiversity commitments, the CBD website states that Jordan’s overall “legislative framework is in place but still requires further development.”Footnote 67 Arguably, this is representative of countries in the MENA region. Thus, very few countries, including the United Arab Emirates (UAE), have developed explicit legal and institutional frameworks on biodiversity and nature conservation in the MENA region.Footnote 68

17.3.2 Marginality of Environmental Law Education on Biodiversity in the MENA Region

A major issue afflicting environmental law education is that it is not part of mainstream legal education in many parts of the world. As Fowler and others aver: “Marginality suggests that a subject sits at the fringes of the discipline of law, is inconsequential, and is seen as a luxury rather than an essential component of a good legal education.”Footnote 69 This is also exemplified in the marginality of environmental law in the legal education curriculum in the MENA region. Well-respected scholars, and numerous reports and surveys, have confirmed that environmental law education is peripheral and is not mainstreamed in the legal curriculum in the MENA region.Footnote 70 Even though environmental education is integrated in the university curriculum in many universities in the MENA region, environmental law education is still lacking in many places. Thus, as alluded to earlier, environmental law is not a core course of study in legal education in many parts of the MENA region. For example, Ahmed Elseidi, one of the leading environmental lawyers in Egypt, suggests: “Unlike the US, Egypt lacks advanced legal education courses that detail environmental rights and justice, hindering citizens from understanding the severity of their country’s issues.”Footnote 71 This exemplifies the current state of environmental law education in some parts of the MENA region. Hence, scholars have alluded to the fact that there are very few higher education institutions with specialist courses (including biodiversity and nature conservation) in the region that promote students’ knowledge and capacity regarding environmental law and related issues including sustainable development.Footnote 72 Furthermore, the marginal status of environmental law in the MENA region exemplifies or ensures that biodiversity awareness and nature conservation is severely lacking in legal education curricula in the region. This is also accentuated by the near absence of specialist biodiversity law courses in the MENA region.

17.3.3 Shortage of Biodiversity and Environmental Law Expertise in the MENA Region

In many parts of the world (especially in MENA countries), there is a shortage of environmental law scholars, especially with expertise and a focus on biodiversity and nature conservation, and this remains a noteworthy barrier to the teaching of the subject in the MENA region.Footnote 73 Thus, in MENA countries, there is an acute shortage of legal expertise on biodiversity and nature conservation and a paucity of legal scholarship on biodiversity and nature conservation. Accordingly, this is also a reflection of the current state of environmental law teaching in the MENA region.

Furthermore, the shortage of biodiversity and environmental law expertise has negative impacts on the development of university law courses or programs focused on biodiversity and nature conservation in the region. This in turn impacts negatively on the promotion of biodiversity awareness in MENA countries.

17.3.4 Resource Constraints

Some of the major issues impacting the successful implementation of environmental education initiatives in the MENA region are resource constraints or challenges, especially regarding the teaching of environmental education and environmental law. The teaching of environmental law requires access to and availability of materials. The teaching materials or resources (which includes textbooks, journal articles, and course materials) on environmental education and environmental law education are mainly in the English language.Footnote 74 In the MENA region, the principal language of teaching is Modern Standard Arabic, and hence some MENA educators regularly “struggle to access the lion’s share of available climate law teaching resources, raising the need for more translation of resources, as well as designing learning resources and platforms in Arabic, to provide greater access to learning resources on climate change law to MENA academics and students.”Footnote 75 Furthermore, some relevant stakeholders at a regional conference in the region have suggested that a major reason for the slow development of environmental law education in the MENA region is the absence of authoritative texts or books focused on environmental law in the region.Footnote 76 However, there is a need for more books and resources explicitly focused on biodiversity laws, nature conservation, and biodiversity awareness in the MENA region.

Closely associated with this are financial constraints that limit the implementation of biodiversity education and awareness programs. In many parts of the world, governments are reducing the budgetary funds allocated for funding environmental education initiatives due to the economic and financial reasons among others.Footnote 77 For example, the COVID-19 pandemic has had negative impacts on funding of environmental projects in the MENA region.Footnote 78 Furthermore, given the economic and income inequalities in the MENA region, some scholars have argued that this makes the MENA region one of the most unequal in the world.Footnote 79 For example, some of the wealthiest countries are found in the MENA region, which is also home to some of the poorest countries in the world. This also has negative impacts, including the disparities in the quality of university education in the MENA region and hence some of the universities in the region are unable to retain and attract experts in the environmental law discipline.Footnote 80 Many of the existing environmental education initiatives in the MENA region are majorly sponsored by international donors and are thereby unsustainable in the long term.Footnote 81

Additionally, the funding of biodiversity and nature projects, including environmental law education initiatives focusing on biodiversity and allied issues, are expensive.Footnote 82 Thus, there is an acute lack of funding for environmental law education initiatives (including educational initiatives focusing on biodiversity and nature conservation awareness) in many MENA countries. Arguably, the lack of funding severely impacts the development of biodiversity and nature conservation awareness initiatives in environmental law education in higher institutions of learning in the MENA region.

17.3.5 Impacts of Conflict on Environmental Education in the MENA Region

The MENA region has for many years remained an epicenter of a series of conflicts and wars.Footnote 83 The region has been affected by a plethora of recent armed conflict and examples include Yemen, Syria, Iraq, and Libya.Footnote 84 Conflict and instability have had negative impacts on education (including environmental education) in parts of the MENA region.Footnote 85 This poses tremendous challenges for educators and students who can end up being displaced and unable to access education sites or safely access educational materials, and thus cannot engage in face-to-face education activities.Footnote 86 Accordingly, conflict in parts of the MENA region is one of the major barriers impacting negatively on the implementation of environmental law education (including educational measures focused on biodiversity and nature conservation) initiatives and policies in the region. Furthermore, a plethora of relevant stakeholders, including academics, have blamed the lack of biodiversity and nature conservation research in the MENA region on the conflicts, poverty, wars, and economic woes affecting some countries in the region.Footnote 87 Thus, governments in the region are prioritizing human needs and fighting poverty rather than developing educational initiatives on biodiversity and nature conservation.Footnote 88 For example, in Iran, Jowkar and others suggest that in the last two decades, environmental protection appears not to be a pressing issue for the government because it is finding it difficult to meet the economic expectations of its citizens.Footnote 89 Thus, in some parts of the MENA region, environmental education (including biodiversity and nature conservation awareness) has been negatively impacted by socio-political factors.

17.4 Strengthening Environmental Law Education on Biodiversity in the MENA Region: Recommendations

Environmental law education can be one of the integral tools or strategies in strengthening the implementation of biodiversity treaties in the MENA region. Some of the recommendations analyzed in this section include mitigating the marginality of environmental law education on biodiversity, integrating or embedding biodiversity awareness in environmental law education, capacity building for environmental law academics, improved funding of environmental education initiatives in the MENA region, and biodiversity litigation as tool for the implementation of biodiversity treaties.

17.4.1 Comprehensive National Policy and Legislation on Biodiversity and Nature Conservation

It is essential that MENA countries enact comprehensive laws and regulations for biodiversity and nature conservation issues to provide clear framework for the implementation, monitoring, and enforcement of biodiversity and natural conservation and allied issues.Footnote 90 Thus, governments in the MENA region need to implement or create “dedicated action plans to halt and reverse the loss of critical habitats and species, enhance water management practices and conserve vital freshwater, and mainstream sustainability and conservation in key social and economic activities.”Footnote 91 Furthermore, MENA countries can take inspiration from the actions and strategies enshrined in the UAE’s framework on biodiversity and nature conservation. For example, the UAE has a comprehensive framework on biodiversity and nature conservation.Footnote 92 The UAE has signed, and in some cases ratified, various international treaties and mechanisms focusing on biodiversity and nature conservation, including the CBD, the Convention on the International Trade in Endangered Species of Wild Fauna and Flora, the Nagoya-Kuala Lumpur Supplementary Protocol on Liability and Redress to the Cartagena Protocol on Biosafety, the United Nations Convention to Combat Desertification, and the Ramsar Convention on Wetlands.Footnote 93 Furthermore, the UAE has a plethora of action plans on biodiversity and nature conservation, including the National Biodiversity Strategy 2014–2021.Footnote 94 Thus, the UAE can be an inspiration to other MENA countries on how to develop a comprehensive legal framework on biodiversity and nature conservation.

17.4.2 Mitigating the Marginality of Environmental Law Education in the MENA Region

Generally, it should be noted that although environmental law is not a core component of the legal education curriculum, this does not necessarily mean that such courses will not have students or academics conducting research on it. For example, in North America and parts of Europe, notwithstanding the elective or noncore status of environmental law, it is quite popular and has a firm place in the legal curriculum, with large numbers of students.Footnote 95 In several developing countries, notwithstanding the elective status of environmental law in the legal curriculum, environmental lawyers and activists have used their expertise of environmental law as means of engaging in social change.Footnote 96 Thus, in the context of MENA countries, environmental law (incorporating biodiversity and nature conservation) should be fully integrated and made a core component of the legal curriculum in the region. This is akin to the move taking place in some developing countries. Therefore, in some developing countries, including Indonesia, the Philippines, India, and China, environmental law is becoming a mandatory or core aspect of the undergraduate legal curriculum.Footnote 97 Mainstreaming environmental law is a key strategy that can be used in promoting environmental law education and this will have positive impacts on enhancing environmental awareness including biodiversity and nature conservation awareness in the MENA region. This is arguably in line with the AFED report on environmental education in the MENA region, that there is an urgent need to reinforce topics including environmental law in the legal education curriculum in the MENA region.Footnote 98 Thus, this will help bring to the fore the relevance or utility of biodiversity awareness and nature conservation in environmental law education in the MENA region.

17.4.3 Embedding Biodiversity Awareness in Environmental Law Education in the MENA Region

Awareness and understanding of biodiversity issues should be embedded in the law curriculum in the MENA region. For example, this can be done via already existing environmental programs offered by universities or as part of the legal education curriculum in the MENA region. Akin to what Bouwer has termed as “climate consciousness” in legal practice,Footnote 99 there should be explicit embedding or integration of biodiversity consciousness or awareness into the legal education curriculum in universities or higher education institutions and in legal practice (especially environmental law practice) in the MENA region. According to Preston: “Climate change places a responsibility on lawyers to adopt a climate conscious rather than a climate blind approach in their daily legal practice. A climate conscious approach requires an active awareness of the reality of climate change and how it interacts with daily legal problems.”Footnote 100 Hence, due to the severe nature of biodiversity threats in the MENA, the legal education curriculum and the training of lawyers should be totally revamped to contain explicit allusions to the utility of international and national legal frameworks on biodiversity, practices, principles, and awareness of biodiversity issues. Arguably, this can play a positive role in the development of legal strategies to help tackle the source of biodiversity threats in the MENA region. Thus, promoting the effectiveness and the implementation of biodiversity treaties in the MENA region will enhance the various measures developed to tackle the sources of the threats to biodiversity.

Furthermore, many laws and policies have been developed in the MENA region for the protection and conservation of biodiversity sources. Thus, law students and lawyers in the MENA region should be supported via environmental law education to understand the implications of these laws and policies and their impacts in the MENA region. Furthermore, students in the MENA region, via biodiversity awareness in environmental law education, will be able to understand that the international conventions on biodiversity are legal mechanisms that create obligations on countries that have ratified the conventions. Thus, countries that have ratified such treaties are expected to adapt their legal frameworks or laws to ensure that all the commitments arising from the international treaties or conventions are met locally.Footnote 101 Arguably, awareness or knowledge of the legal implications of biodiversity treaties “provides the student with a standpoint from which to critically assess the behavior of governments, parliaments, authorities, and businesses,”Footnote 102 regarding the implementation of biodiversity treaties in the MENA region. Furthermore, by virtue of Article 27 of the Vienna Convention on the Law of Treaties, contracting parties or countries to treaties cannot rely on national laws as reasons or justifications for not respecting their expected obligations or commitments under such treaties. Thus, MENA countries should adhere to the various obligations arising from the plethora of international conventions relating to biodiversity and nature conservation and other allied issues that they have signed and ratified.

Awareness of the legal frameworks on biodiversity is not enough; society (especially lawyers and university law students) in the MENA region should also develop a deep understanding of how biodiversity will be influenced and shaped by society’s response to biodiversity threats in the region.Footnote 103 This will arguably lead to improving of the skill sets or expertise of lawyers regarding biodiversity awareness or biodiversity-related issues in the MENA region.

Furthermore, according to Hulme, international conventions relating to biodiversity issues or “nature conservation treaties include mandatory obligations to conduct conservation training and education.”Footnote 104 For example, Article 27 (1) of the World Heritage Convention (WHC) 1972 explicitly accentuates the relevance of states engaging in the awareness of natural heritage issues to “strengthen appreciation and respect by their peoples.”Footnote 105 This arguably serves as a mobilization tool for society to support and value its conservation and natural heritage protection.Footnote 106

This chapter adopts the view of Lavey on the utility of climate change education integration into law school curriculum,Footnote 107 and this is also applicable to biodiversity awareness expected from environmental lawyers within the MENA region. Thus, Lavey suggests that effective lawyering premised on knowledge, skills, and understanding regarding the various risks from undulating environmental conditions should underpin legal education.Footnote 108

Furthermore, in the context of biodiversity and nature conservation, effective lawyering should also be underpinned by knowledge and awareness of the biodiversity and nature conservation issues in the MENA region. Hence, legal practitioners in MENA countries should be at the forefront of biodiversity consciousness or awareness in their legal practice in the MENA region. Additionally, UNESCO avers that “[e]ducation is essential for the sustainable and equitable use of biodiversity and its conservation. It is also crucial for mainstreaming biodiversity.”Footnote 109 Thus, environmental education is essential to actualizing the SDGs (especially SDG 15) in the MENA region.Footnote 110 Additionally, leading scholars on environmental law in the MENA region at a conference in 2018 advocated for the explicit integration of environmental law (which also includes biodiversity and nature conservation) in the higher education curricula in the region.Footnote 111

17.4.4 Capacity Building of Environmental Law Academics

Different initiatives have been developed in the MENA region to mitigate the shortage environmental law scholars, improving the skill sets of academics and various stakeholders, including UNEP and ASSELLMU.Footnote 112 For example, UNEP in collaboration with various stakeholders have played a crucial role in the expansion of international environmental law and principles and has supported different countries in developing and enhancing capacities or expertise in environmental law.Footnote 113 Regarding environmental law education, UNEP has supported various initiatives to develop environmental law education in different parts of the world, including Africa, Asia, and the MENA region.Footnote 114 For example, UNEP in collaboration with Professor Olawuyi was instrumental in the creation of the ASSELLMU in 2018. The ASSELLMU is a professional network of environmental law scholars and one of its major objectives is conducting research on the practice and implementation of environmental law in the region.Footnote 115 Since its inception, the ASSELLMU has organized several conferences that have served as avenues or platforms for bringing environmental law teachers, practitioners, lawyers, and trainers together to exchange knowledge with each other.Footnote 116

As one of the strategies of improving the skill sets of environmental law scholars and teachers in the region, ASSELLMU has also organized a series of events and developed the teaching of environmental law toolkits. For example, the Training Manual for the TTT Program in Environmental Law for Higher Education Institutions in the MENA Region, which was jointly organized by the UNEP and ASSELLMU.Footnote 117 This training program was developed to support academics conducting research or teaching environmental law-related courses or programs in the MENA region. Furthermore, the “overarching objective of this TTT Programme is to enhance the technical capacity for environmental law education in MENA universities through an in-depth exploration of innovative approaches for curriculum design, teaching pedagogies, and student assessment.”Footnote 118 Thus, the regular occurrence of this and similar capacity-training events will continually improve the skill sets of environmental law scholars and arguably help in mitigating the shortage of environmental law experts in the region. Additionally, specialist training should be organized for environmental law scholars and lawyers to enhance their knowledge and pedagogy relating to biodiversity law and awareness and nature conservation in the MENA region. For example, ASSELLMU, UNEP, and other relevant stakeholders should explicitly embed the knowledge of biodiversity laws, awareness, and nature conservation issues in their training courses. These training courses should be organized for environmental scholars, lawyers, and policymakers in the MENA region to deepen their knowledge or understanding of biodiversity and nature conservation issues. Furthermore, continuous training of environmental law teachers, researchers, and academics will enhance the delivery of environmental law education programs in universities in the MENA region.

17.4.5 Improved Funding of Environmental Education Initiatives in the MENA Region

There is a need for increased funding of the ASSELLMU and other similar environmental education initiatives (including biodiversity and nature conservation) in the MENA region. The funding of environmental education initiatives and environmental programs is said to be on the decline in several states in the MENA region.Footnote 119 The number of environmental initiatives is on the rise in the MENA, and this needs increased funding from the government and other relevant stakeholders for these initiatives to be successfully implemented. Hence, the AFED report suggests that financial resources ought to “be raised independently of international donors in order to enhance both the quality and evidence base of environmental topics.”Footnote 120 Furthermore, richer MENA countries, including Saudi Arabia and the UAE, have an integral role to play by funding environmental education initiatives (including those focused on biodiversity and nature conservation) in other MENA countries.

17.4.6 Mitigating Impacts of Conflicts on Environmental Education Initiatives

The movement to online teaching and use of technology could help improve access to environmental education by students during conflicts in the MENA region. Thus, online-learning platforms can serve as lifeline for students in MENA, whose education has been negatively impacted by the conflict.Footnote 121 Consequently, this requires reliance on technology and if the computer network is able to cope with the demands and if the students affected by conflict can get online, they can potentially access education.Footnote 122 The COVID-19 pandemic has shown the world (especially the education sector) that online-learning platforms can serve as good alternatives to face-to-face teaching and many schools and universities have fully embraced the technology to enable access to education and its resources, during and even after the COVID-19 pandemic, including in the MENA region.

Furthermore, the reliance on online teaching and use of technology can improve access and create open more opportunities for environmental law education focusing on biodiversity and nature conservation awareness in the region. For example, more people can be trained through online or virtual learning platforms on the utility of biodiversity and nature conservation awareness in the MENA region. Also, various online tools such as videos, e-learning tools, and other educational technology resources can enhance the quality of the learning and teaching of biodiversity and nature conservation issues in the region.Footnote 123

17.4.7 Biodiversity Litigation as a Tool for the Implementation of Biodiversity Treaties in the MENA Region

Due to the failings and weaknesses of domestic and international regulatory mechanisms in different parts of the world, the use of litigation is now regularly relied upon by individuals, victims, and other relevant stakeholders in holding governments, multinational corporations, and other entities accountable for their actions in different parts of the world.Footnote 124 For example, due to the existing weaknesses in the global climate governance regime, climate litigation has become a popular strategy or mechanism utilized by climate change victims and their representatives in various jurisdictions in both developing and developed countries in holding multinationals and states accountable for climate inaction.Footnote 125 Arguably, due to the impact of climate litigation at the national and international levels, some scholars have argued for the development of biodiversity litigation as one strategy that can be relied upon to enhance the implementation of the various biodiversity conventions at the domestic level.Footnote 126

There are different definitions and conceptualizations of biodiversity litigation.Footnote 127 However, this chapter adopts the definition by Futhazar et al., and they define biodiversity litigation as “any legal dispute at the national, regional or international level that concerns conservation of sustainable use of and access and benefit-sharing to genetic resources, species, ecosystem and their relations.”Footnote 128

There is the potential or possibility for biodiversity litigation to hold governments accountable for their international biodiversity commitments within MENA. Successful biodiversity litigation has taken place in other developing countries, including India, Brazil, and Tanzania.Footnote 129 However, biodiversity litigation remains largely untested in the MENA region. Environmental biodiversity awareness can improve the knowledge or expertise of litigants and other relevant stakeholders in successfully exploring the potential of biodiversity litigation to seek redress for landscape alteration and habitat degradation resulting from development activities and projects in the MENA region. Reliance on litigation as a legal strategy has achieved some success in transnational human rights litigation instituted against multinational corporations and governments in different parts of the world.Footnote 130 Successful litigation can have positive impacts on the regulation of different sectors or industries in countries.Footnote 131 Thus, successful biodiversity litigation could strengthen the implementation of biodiversity treaties in the MENA region.Footnote 132

17.5 Conclusion

Various international and regional instruments and policies have underscored the importance of environmental education in advancing biodiversity and nature conservation. In the MENA region, there has been an in increase in the number of environmental education initiatives; however, environmental law education (including initiatives on biodiversity and nature conservation) is still at the fringes of the university curriculum in the region.

This chapter has undertaken a critical analysis of the current state of environmental law education in the MENA region. Notwithstanding the marginal status of environmental law education in several countries in the region, it can serve as one of the strategies to strengthen the implementation of the plethora of biodiversity treaties in the region. Several recommendations are made in this chapter on how to improve the status of environmental law education in the region and these measures can be replicated in other developing countries as well. The recommendations include mitigating the marginality of environmental law education, embedding biodiversity awareness in environmental law education, the capacity building of environmental law academics, improved funding of environmental education initiatives, mitigating the impacts of conflicts on environmental education initiatives, and the utility of biodiversity litigation. Arguably, the implementation of these recommendations, which are premised on environmental law education in MENA countries, will enhance and localize the implementation of biodiversity treaties in the region.

18 Advancing the Nexus Approach to Biodiversity and Nature Conservation in the MENA Region Summary and Options for Policymakers

Damilola S. Olawuyi
18.1 Introduction

This book examines the values, assumptions, and guiding principles that underpin biodiversity and nature conservation law and policy in the MENA region. With case studies from various MENA countries, the book explored the applicable legislation and institutions, as well as emerging innovative and bottom-up approaches for the implementation of biodiversity and nature conservation treaties across the region. This final chapter reviews the salient themes that have been discussed and identifies directions for future action and research.

The MENA region, like many parts of the world, is facing a rapid biodiversity loss emergency.Footnote 1 Apart from the threats of extinction of rare plants and animal species needed to sustain a functional ecosystem, MENA countries face increased threats of losing access to rare natural and cultural capital required to support medical innovation, tourism, bio-business and trade, biodiversity entrepreneurship, and economic diversification.Footnote 2 Consequently, responding to the current and anticipated social, economic, environmental, and cultural impacts of nature and biodiversity loss is squarely at the forefront of the political and legislative agenda across the region. However, despite the rise in policy formulation on biodiversity and nature conservation, the pace of implementation remains uneven across the region – in terms of having comprehensive laws, policies, training, and harmonized institutions on biodiversity and nature conservation. There is a need for a detailed and up-to-date assessment of emerging regulatory approaches to biodiversity and nature conservation across the region to achieve greater clarity, coherence, and integration. This book is an attempt to meet this need.

The eighteen chapters of this book explore the latest developments of biodiversity and nature conservation law and policy across the MENA region, with a focus on the key legal innovations for the sustainable management of the region’s rich natural and cultural heritage. The chapters have also explored larger questions on legal and institutional frameworks that can help address broader issues of inadequate protection of land rights in nature-based programs, gender inequality, inadequate stakeholder engagement, lack of transparency, limited access to environmental information, and the inadequate scope of available financing for biodiversity programs. The case studies have also explored innovative legal strategies to address these misalignments and gaps.

This final chapter offers reflections on the case studies. It addresses how lessons from the diverse jurisdictions may inform thinking on how MENA countries can advance existing national strategies and visions on biodiversity and nature conservation through clear and comprehensive legislation. Considering the wide-ranging impacts of biodiversity loss on water, energy, and food security, as well as on cultural heritage, tourism, urban planning, healthcare, human rights, and other key sectors, comprehensive and wide-ranging responses are required. However, as shown in the case studies in this book, sectoral and piecemeal efforts on biodiversity and nature conservation have been prevalent in many MENA countries. This has not fostered a holistic consideration of the interplay and trade-offs between biodiversity and conservation programs and other key sectors and systems, especially the biodiversity, climate, water, energy, and food and health nexus.Footnote 3 A failure to situate biodiversity as a fundamental aspect of advancing climate action, ensuring water, energy, and food security, as well as combating pandemics and the spread of diseases, may result in overall ineffectiveness. Therefore, greater effort is required to mainstream biodiversity and nature conservation into all aspects of development planning and decision-making, in order to effectively anticipate and address short- and long-term drivers and impacts of biodiversity loss and enhance benefit-sharing in a holistic manner.

This chapter discusses essential steps for mainstreaming biodiversity and nature conservation into all aspects of governmental decision-making across the MENA region. After this introduction, Section 18.2 discusses legal and institutional reforms that could advance legal preparedness for biodiversity and nature conservation in the region. Section 18.3 is the concluding section.

18.2 Mainstreaming Biodiversity Plans and Strategies into Decision-Making Processes in the MENA Region

There is an urgent need for all MENA countries to establish coherent and holistic governance frameworks that mainstream and advance the cross-sectoral protection of all aspects of nature and biodiversity, including forests, wildlife, wetlands, fisheries, natural habitats, and protected areas, in development planning.

Biodiversity mainstreaming refers to the process of integrating biodiversity considerations into all aspects of development planning and policymaking.Footnote 4 As far back as 2016, the 13th Conference of the Parties (COP) to the Convention on Biological Diversity (CBD) in its Decision XIII/3, called on parties and other stakeholders to “mainstream conservation and sustainable use of biodiversity within and across various sectors, including, agriculture, forestry, fisheries and aquaculture and tourism at all levels and scales” in order to achieve the Aichi Biodiversity Targets.Footnote 5 Under this model, biodiversity impacts are carefully considered in an integrated manner to ensure that programs and actions in one sector do not create other adverse impacts in other sectors of the economy. For example, many world heritage sites that play important roles in the tourism sector are also key biodiversity hubs.Footnote 6 The process of designing legislation and policies on cultural heritage should therefore include a clear linkage to biodiversity, including tailored frameworks that protect heritage sites from activities that may harm biodiversity. Similarly, given the potential impacts of the food and agriculture sector on land alteration and the degradation of natural habitats, holistic frameworks are required to advance sustainable agricultural practices and technologies to support biodiversity and nature conservation.Footnote 7 Likewise, through agroecology – “an approach to agriculture that harnesses biodiversity to build complex, low-impact agricultural systems” – the benefits of biodiversity-focused farming can be harnessed to enhance food security.Footnote 8 Mainstreaming biodiversity and nature conservation is therefore essential not only for advancing environmental objectives but also for accelerating social and economic objectives, including food security, trade, economic diversification, and equitable access to land and natural resources, as well as the all-round fulfillment of human rights.

This section discusses seven important steps that could help stakeholders across different sectors to effectively consider and mainstream biodiversity and nature conservation into all aspects of decision-making.

18.2.1 The Need for Holistic Law and Policy Responses

As discussed in Chapter 2, several MENA countries have released their National Biodiversity Strategies and Action Plans (NBSAPs).Footnote 9 Some of these NBSAPs address the intersections of biodiversity and nature conservation with all other key sectors, ranging from human rights, to food, water, energy, education, aviation, and healthcare, among other things.Footnote 10 They also set out broad plans to integrate biodiversity targets into all aspects of national development policies and reporting. However, despite the release of NBSAPs across the region, clear and comprehensive laws and policies that integrate biodiversity in all key sectors are yet to be fully articulated across key sectors. There remains a clear need for legally binding requirements and targets for stakeholders to mainstream biodiversity and nature conservation, especially nature-based solutions, in all aspects of investment and planning. For example, as discussed in Chapter 8, it is important to integrate a public health perspective into biodiversity planning and policymaking to effectively address the spread of zoonotic diseases such as the COVID-19 pandemic. It is equally important to integrate water management perspectives into biodiversity law and policy to address the impacts of water scarcity and aridity on biodiversity, while also leveraging nature-based solutions to improve water management.Footnote 11 Human rights considerations are also important to avoid reactionary responses that may exacerbate land grabs, gender inequity, and other human rights concerns while tackling biodiversity loss.Footnote 12 Without an integrated policy response, nature-based programs and projects designed to address biodiversity loss may exacerbate social exclusions, human rights violations, food, water, and energy injustice, environmental impacts, and conflicts in already vulnerable communities.Footnote 13

Therefore, there is an urgent need to strengthen synergies and policy coherence in the design, approval, financing, and implementation of biodiversity and nature conservation programs and policies across all sectors through an integrative approach. Biodiversity can no longer be addressed from a narrow sector-by-sector lens. Rather, biodiversity must be paramount in policy and decision-making at all levels of government. For example, the CBD’s National Reporting Guidelines require countries to provide evidence of “how biodiversity is reflected in poverty reduction strategies and other key cross-cutting policy instruments, and into the various economic sectors.”Footnote 14 This entails biodiversity proofing all development and investment strategies, plans, and programs to minimize damage to ecosystems while maximizing conservation.Footnote 15 Such systematic proofing of polices to address their biodiversity and ecosystems impacts will not only maximize conservation but could also accelerate the widespread implementation of nature-based solutions that advance co-benefits and synergies in climate change mitigation and other sustainability efforts.Footnote 16

18.2.2 Clear and Comprehensive Legislation on Biodiversity and Nature Conservation

Second, mainstreaming biodiversity into all aspects of governance and decision-making will require clear regulatory frameworks on biodiversity and nature conservation. As seen from the case studies, one key limitation to halting biodiversity loss across the region is the absence of specific biodiversity legislation in many MENA countries. Some of the legal obligations to protect and conserve biodiversity can be inferred or drawn from general environmental legislation, national visions, and other policy documents. However, such an approach is indeterminate and may not provide an opportunity for a clear and robust understanding of the critical interplay, trade-offs, and synergies that exist in decision-making and planning across the diverse domains impacted by biodiversity loss in the short and long term.

For example, the lack of comprehensive biodiversity legislation often means that several of the obligations relating to biodiversity proofing and the use of market-based mechanisms in biodiversity programs are found in different segregated and compartmentalized pieces of legislation or instruments. Some of these instruments may not specifically refer to important concepts such as biodiversity proofing, biodiversity financing, biodiversity-relevant taxation, biodiversity entrepreneurship, or the use of market-based mechanisms to halt biodiversity loss, which may limit their scope of application and implementation.Footnote 17 Consequently, while the need for biodiversity and nature conservation is generally clear, the granularity of what it requires in practice remains unclear. This creates interpretation gaps on the legal basis and source of responsibility when it comes to supervising different aspects of national biodiversity actions and strategies. Clear, comprehensive, and specific legislation is critical to effectively mainstream biodiversity and nature conservation into the policy apparatus of governments at all levels.

As the Taskforce on Nature-Related Financial Disclosures recommends, biodiversity governance should emphasize four key actions: avoid, reduce, restore, and regenerate (the AR3T framework).Footnote 18 First is the need to avoid damage to nature and ecosystems through biodiversity-supportive steps such as conducting environmental impact assessments and strategic assessments to protect biodiversity. Second is the need to reduce or minimize likely adverse impacts to biodiversity that cannot be avoided. For example, leveraging biodiversity-smart infrastructure (i.e. buildings, technologies, and systems that reduce biodiversity loss and trade-offs, and enhance conservation) across all key sectors can significantly reduce the risk of biodiversity loss. Third is the need to restore and recover species or ecosystems that may have been degraded or diminished. For example, specific efforts to replace endangered species such as the Arabian oryx have resulted in sustained progress over the years resulting in its removal from the list of endangered species in the MENA region.Footnote 19 Such efforts should be integrated into biodiversity strategies and policies to ensure that they are sustained. Fourth is the need to regenerate or increase the productive capacity of the ecosystem in order to sustain biodiversity. Regenerative practices aim to improve, rehabilitate, and support the natural functioning of the ecosystem.Footnote 20 For example, regenerative agriculture has been discussed in studies as a “sustainable land management practice” focused on ecological functions.Footnote 21

A clear legal framework on biodiversity could provide the legal basis and obligations for project planners and stakeholders to integrate the AR3T framework into project development and implementation. For example, biodiversity legislation can mandate the biodiversity-inclusive environmental impact assessment and strategic environmental assessment needed to promptly spot and address adverse impacts of projects on biodiversity.Footnote 22 Biodiversity legislation can also provide project developers and planners with clarity on the key design standards and measures to comply with at the project design and approval stage. Given the urgency and need to halt biodiversity loss, clear and specific biodiversity legislation could streamline the approval of nature-focused investments and provide incentives for private sector participation, especially in priority biodiversity restoration projects.Footnote 23 Biodiversity legislation could also be the basis for clarifying the regulatory models that will underpin integrated response in a country. As Dimitropoulos and Lokhandwala note, there are three major regulatory tools to help transition toward more sustainable development policy choices: command-and-control, market-based approaches, and nudges.Footnote 24 MENA countries will need to carefully consider complex socio-economic conditions in their countries and develop a responsive legal framework that provides an effective avenue to accelerate their NBSAPs in a cost-effective manner.

18.2.3 Frameworks to Enhance Fair and Equitable Access and Benefit-Sharing

As discussed in Chapter 9, while there is a growing awareness regarding biodiversity and nature conservation across the MENA region, the development of clear and comprehensive regulatory frameworks on access and benefit-sharing (ABS) have been slow across the region. Challenges such as a lack of awareness regarding ABS, a lack of statistical data on ABS, and an inadequate level of compliance with international frameworks on ABS linger across the region, highlighting a continuing need for advancing awareness, fine-tuning legal frameworks, and fortifying implementation measures.

Improving regulatory regimes on biodiversity in general, and ABS in particular, requires a legal, fiscal, and institutional reform agenda aimed at maximizing the full value of ABS across the region. This would be done by developing and implementing comprehensive standards that enhance the access, utilization, and benefit-sharing of genetic sequence data. A starting point is for MENA countries to include clear provisions on ABS in biodiversity legislation to ensure the sustainable use of the region’s extensive genetic resources for current and future generations. Aligning such legislation with international standards can enable MENA countries to leverage their comparative advantage as the location of important genetic resources needed globally to advance agriculture, conservation, research, and trade.

Furthermore, it is imperative for regulators and industry associations to collaboratively design model contracts and toolkits that define and conceptualize essential provisions on ABS to be included in research and development (R&D) and technology development contracts. Such clarity will enable countries to strike a much-needed balance between ensuring the use of genetic resources for R&D, pharmaceutical, agricultural, and other innovation efforts and preventing abuse and ensuring that benefits resulting from such use are accessed by local communities in a just and equitable manner. Establishing standard contractual provisions relating to data disclosure, reporting, and the allocation of genetic resources and their benefits could clarify expectations and enable all stakeholders to ensure the equitable distribution of the dividends derived from genetic resources. For example, the Swiss Academy of Sciences has developed a template ABS agreement that includes important terms for allocating rights, benefits, and risks with respect to genetic resources in a fair and equitable manner.Footnote 25 Similarly, the Chancery Lane Project has developed standard contractual clauses with biodiversity-focused provisions that address a wide range of themes including regenerative farming and soil preservation.Footnote 26 Integrating such clauses and provisions in investment contracts, especially land-based investments in agriculture, extractives, and the pharmaceutical and construction sectors, is essential to improving current understanding on just and equitable ABS.

Likewise, lawyers providing counsel on development projects should not only integrate ABS provisions in contracts; they should also advise clients on the importance of managing risks related to the use of genetic resources in local communities in order to avoid disputes and conflicts. Indigenous communities are increasingly insistent on ensuring that their traditional knowledge and genetic resources are used in a fair, inclusive, and just manner in line with international law standards.

18.2.4 Institutional Coherence and Coordination

In addition to developing a clear and comprehensive legal framework on biodiversity and nature conservation, establishing the right institutional setup for the practical coordination and cooperation of the diverse stakeholders and institutions will also be essential.Footnote 27 While rapid biodiversity loss would affect different sectors, the process of coordinating responses across different agencies and institutions that could be impacted has not been straightforward. Due to the different mandates, priorities, and financial resources between ministries, the attention and focus on mainstreaming biodiversity into their strategies, policies, and programs varies significantly. Consequently, biodiversity and nature conservation programs continue to be implemented and articulated in a largely sectoral and fragmented manner.Footnote 28 This makes it complex and difficult to achieve institutional coherence and coordination of efforts across ministries and agencies in the design and implementation of biodiversity policies and responses. Furthermore, the implementation of intersectoral coordination is often stifled by capacity questions. For example, mainstreaming biodiversity into the work of human rights agencies or food ministries would require expanding staff capacity or recruiting experts in biodiversity and environmental science. Similarly, biodiversity-proofing infrastructure development projects by public works authorities could require recruiting staff that can understand, analyze, and implement biodiversity-related legislation and policies. Given that several of these institutions are currently not constituted or designed to analyze and implement biodiversity and nature programs, their ability to effectively analyze and implement different biodiversity-related information and data may be limited by differences in skill sets and expertise.Footnote 29 Also, epistemic distinctions and lack of operability by different actors and institutions is fueled by the divergent training, styles, and perspectives of the actors in their respective sectors and fields.Footnote 30

These problems raise the need for greater interoperability and standardization approaches that foster cooperation and minimize duplication among sectors and actors in the design and implementation of climate change projects and programs. As recommended by the CBD, the process of designing NBSAPs is an important starting point for engaging widely with key institutions and stakeholders, including government ministries and departments, business enterprises, civil society, academia, and other key relevant entities that have prominent roles to play in advancing biodiversity and nature conservation programs.Footnote 31 Such an early and widespread multistakeholder engagement process is required to secure the commitment of all key institutions and entities. National dialogue should be promoted and aimed at building shared and common understanding on nexus and integrated biodiversity proofing by institutional actors in various sectors. Such dialogue will examine to what extent the mandates of existing institutions are coherent, conflicting, and/or duplicative and also whether there are linked platforms in place to support knowledge and information sharing and intersectoral cooperation on biodiversity and nature conservation. For example, institutions can leverage their respective expertise, facilities, and best practices by engaging with staff and experts across sectors to assist with reviewing and assessing the implication of multisector projects on natural and cultural heritage. Inter-agency linkages and partnerships, through joint initiatives and knowledge sharing, could increase trust and enhance synergistic solutions that encourage coherent responses to identified threats. Furthermore, such dialogue should aim to address barriers to interoperability by promoting the information sharing and knowledge exchange on biodiversity and nature conservation by all relevant ministries and agencies in open and linked systems, as well as constituting cross-sectoral panels and committees that can provide an informed picture of biodiversity mainstreaming efforts across the country.

18.2.5 Increased Biodiversity Financing and Investment

Linked to the question of capacity and institutional coordination is the question of resources. While there is increased awareness on the need for nature-based solutions to halt rapid biodiversity loss across the region, access to financial resources, especially by small and medium eco-enterprises, to advance biodiversity entrepreneurship remains a key challenge.Footnote 32 Chapter 11 unpacks the key role of innovative financing approaches, such as Islamic financing, to meet the currently huge financing challenges that face biodiversity-related investments in the MENA region. Legal and governance gaps that stifle the application of Islamic financing, crowdfunding, and other financing tools in different MENA countries must be carefully mapped and addressed in order to support the accelerated development of nature-based solutions and biodiversity projects across the region.

Furthermore, there is a need for increased budgetary allocation and spending on biodiversity programs in the MENA region. Leveraging biodiversity-smart infrastructure across all key sectors will come at a considerable cost.Footnote 33 For example, the cost of upgrading existing infrastructure, expanding current institutions, staffing, training, field inspections, project review panels, and program design will require MENA countries to unlock investment from private and public sectors.Footnote 34 MENA countries can leverage the significant revenue from extractive industries to drive investment in biodiversity-smart development and nature conservation, especially by accelerating nature-focused innovation. With infrastructure spending in the Gulf region alone projected to reach US$200 billion over the next ten years, MENA countries have expressed the political will to invest income from extractive industries to advance knowledge-based economies.Footnote 35 For example, Qatar is developing a Biodiversity Genome Program aimed at enhancing statistical data on genetic resources in the country.Footnote 36 This is in addition to the wide range of conservation projects in the country, such as the lizard biodiversity conservation project, which aim to protect animals that are rapidly becoming endangered such as the Arabian oryx, sand gazelle, ostrich, bustard, and wild rabbit.Footnote 37 Saudi Arabia has also launched a number of biodiversity and conversation projects, such as the Red Sea Biodiversity Project, aimed at halting the loss of rare flora and fauna in the Red Sea and across the country, as well as boosting ecotourism.Footnote 38 Morocco, Bahrain, Oman, Jordan, and the United Arab Emirates have announced similar biodiversity-related projects, including mountain conservation and payment for ecosystem services (PES) initiatives.Footnote 39 If these programs and visions are effectively implemented and sustained, MENA countries could be well placed to achieve biodiversity-smart development, while also achieving socio-economic outcomes such as increased ecotourism, biodiversity entrepreneurship, biodiversity innovation and technology development, and green employment opportunities, including jobs relating to mountain and oasis conservation.Footnote 40

There is a great opportunity for MENA countries to leverage savings from the extractive industries to finance biodiversity programs. For example, MENA countries are home to some of the largest sovereign wealth funds (SWFs) across the world.Footnote 41 Such SWF portfolios can provide opportunities for MENA countries to invest in assets and projects worldwide to halt biodiversity loss. For example, the Qatar Investment Authority, Kuwait Investment Authority, the Public Investment Fund of the Kingdom of Saudi Arabia, and the Abu Dhabi Investment Authority are founding members of the One Planet SWF Working Group, which aims to integrate climate change analysis and environmental considerations in investment decisions.Footnote 42 Through this commitment, MENA countries aim to allocate SWF investments to finance sustainability initiatives, including nature conservation programs. By integrating biodiversity considerations into the design, financing, and implementation of SWF investments, MENA extractive industries can significantly accelerate the attainment of the Sustainable Development Goals (SDGs) relating to biodiversity and nature conservation domestically and abroad.Footnote 43

Furthermore, investing in research and innovation can provide MENA countries with the homegrown and state-of-the-art technologies and tools needed to effectively boost nature-based innovations that support biodiversity and conservation efforts. For example, Saudi Arabia’s biodiversity research project at the King Abdullah Science and Technology University aims to enhance biodiversity-related innovation and research.Footnote 44 MENA countries will need to develop similar sustained research and innovation efforts that can accelerate and support biodiversity-smart development across the region.

18.2.6 Innovative Pedagogies to Accelerate Biodiversity Education

Sixth, the rise of biodiversity and nature conservation law and policy across the region raises the need for innovative pedagogies to train and prepare future lawyers and administrators for evidence-based policymaking in this important field. As discussed in Chapter 17, addressing the rapid loss of biodiversity across the region will require innovative and disruptive teaching methods. The author notes that “there is a need for more specific and tailored workshops and TTT programs on biodiversity in the MENA region to further promote the integration of biodiversity awareness into environmental legal curricula in the various universities and higher education institutions within the MENA region.” This will require law schools across the region to design tailored courses that provide practical and skill-based learning on biodiversity and nature conservation using a wide range of online and in-class tools. Similarly, in developing biodiversity law and policy courses, it is particularly important to adopt enquiry-based learning methods that will integrate practical skills and knowledge and prepare students to engage in real-world problem solving.Footnote 45 For example, biodiversity-related courses should clearly emphasize practical aspects, such as the development and implementation of biodiversity strategies, drafting and negotiating ABS agreements, implementing green building and efficiency standards, and data collection and analysis on biodiversity.

Furthermore, MENA environmental law academics will need to pool their intellectual resources to cooperate in research and capacity development that advance biodiversity and nature conservation. Successful partnerships are necessary to achieve all aspects of sustainable development. This is well recognized by the SDGs; Target 17.9 encourages countries to enhance international partnerships and support to implement all of the SDGs and develop north–south, south–south, and triangular cooperation.Footnote 46

Target 15.C also encourages countries to “enhance global support for efforts to combat poaching and trafficking of protected species, including by increasing the capacity of local communities to pursue sustainable livelihood opportunities.”Footnote 47 Similarly, under Target 4.7 countries are to “ensure that all learners acquire the knowledge and skills needed to promote sustainable development, including, among others, through education for sustainable development and sustainable lifestyles.”Footnote 48 These goals and targets emphasize the need for environmental law academics to continue to develop collaborative research and teaching initiatives that could expand the development of innovative courses on biodiversity and nature conservation law and policy. This type of collaboration was in mind when the Association of Environmental Law Lecturers in Middle East and North African Universities (ASSELLMU) was established in 2018, to serve as a professional network for all MENA environmental law academics.Footnote 49 As stated in its Constitution, ASSELLMU aims to provide a forum for the discussion and dissemination of environmental law in the MENA region and to identify and search for MENA solutions to the region’s environmental problems. It also aims to “spearhead collaborative and multi-disciplinary projects to foster increased awareness for environmental problems, among students and people in MENA region.”Footnote 50

Since its establishment, ASSELLMU has organized a number of conferences and events that aim to enhance knowledge dissemination and information exchange on biodiversity.Footnote 51 It is important for international organizations, private sector actors, and governments across the region to provide technical and financial support to sustain such important efforts. ASSELLMU, and similar cooperative networks, will need to work with education stakeholders, such as ministries of education, as well as private and public sector organizations, to identify essential executive courses for the development of professionals working on nature and biodiversity-related projects. Educators can then develop a blend of practical and theoretical courses to provide lifelong learning opportunities for stakeholders tasked with designing and implementing biodiversity and nature conservation programs.

18.2.7 Need for Biodiversity-Focused Due Diligence

The rise of biodiversity and nature conservation law and policy in the MENA region increases the need for business enterprises and private actors to anticipate and address biodiversity-related legal risks in their investments and projects. Biodiversity-focused due diligence is the process through which enterprises and public actors investigate the direct and indirect the impacts of their investments and projects on biodiversity in order to avoid legal risks.Footnote 52 Legal risks in this context refer to the risk of financial, reputational, or investment loss, legal liability, or dispute settlement costs to a company or institution that may arise from the failure by a business enterprise to mitigate the direct and indirect impacts of biodiversity loss.Footnote 53 Direct or indirect contributions to biodiversity loss can result in significant financial, reputational, and disclosure risks for a business enterprise or entity, especially an entity that fails to comply with emerging laws and policies in this area.Footnote 54 For example, failure to comply with disclosure requirements relating to the impacts of a business or investment on biodiversity may result in fines and sanctions.Footnote 55 On the other hand, the implementation of development projects that adversely impact landscapes, forests, and ecosystems may also trigger lawsuits from impacted communities. For example, investing in NBS and emissions reduction schemes, such as clean development and Reducing Emissions from Deforestation and Forest Degradation projects may result in adverse impacts on human rights, especially through displacements of local communities from their lands and forests, the exclusion of women and youth from decision-making processes, a lack of transparency and accountability, and the inadequacy of judicial remedies for victims.Footnote 56 There is a marked increase in the number of cases in different parts of the world that seek to establish the legal and human rights liability of business enterprises for failing to address biodiversity loss.Footnote 57

As more MENA countries adopt biodiversity and nature conservation legislation and policies, similar arguments may be made before the courts. Over time, failure to effectively anticipate and manage biodiversity-related risks could carry significant financial, legal, and reputational risks for business enterprises operating in the MENA region. Such risks may manifest in the form of the disruption, suspension, or closure of projects by supervisory bodies, hefty regulatory fines, and director and shareholder liability, and may impact a company’s profitability or ability to maintain a license to operate.Footnote 58 Businesses can avoid the increasing backlash associated with biodiversity risks by integrating biodiversity considerations into investment analysis and management processes. Business enterprises in the MENA region, especially those in the extractive and construction sectors, can enhance their capacity to effectively anticipate and manage biodiversity-related risks by participating and engaging with the wide range of voluntary initiatives that aim to support companies to “integrate biodiversity conservation into their internal business practices and operations.”Footnote 59

There is also a need to implement comprehensive biodiversity-focused environmental impact assessments that spot and address biodiversity risks prior to commencing development and investment activities.Footnote 60 Furthermore, human rights impact assessments and due diligence can enhance the abilities of planners to identify and address the potential adverse impacts of biodiversity programs on human rights, especially the right to a clean, healthy, and sustainable environment, land rights, gender injustice, and inadequate public participation in the implementation of such programs.Footnote 61 For example, as discussed in Chapter 4, the loss of forests and other protected areas can trigger several violations of indigenous rights in communities that depend on such resources for their survival, culture, and religion. There is therefore a strong business case, in terms of cost, reputation, and effectiveness, for business enterprises and other actors to integrate biodiversity-focused human rights due diligence in their investment planning and business decision-making, even if the domestic law is silent on such requirements. Adopting sound internal screening processes, as part of corporate due diligence and investment risk management frameworks, could help enterprises to anticipate, mitigate, and address the implications of their investments and projects on biodiversity and ecosystems.

As for the role of lawyers representing companies and investors in transactions and projects, it is important to clarify and emphasize the need for biodiversity and human rights due diligence at early stages of such investments. International bodies and courts insist that business enterprises have a responsibility to address potential and actual adverse human rights impacts across the entire value chain of their operations.Footnote 62 As a result, companies, investors, lenders, and insurance underwriters must appropriately investigate, assess, and price biodiversity-related risks that may arise in the transactional context.

As the Taskforce on Nature-Related Financial Disclosures notes, “nature-related risks and opportunities arise from an organisation’s dependencies and impacts on nature.”Footnote 63 Such biodiversity risks may be physical, transition, and disclosures related. Physical risks may flow from activities or investments that adversely impact biodiversity or from the potential loss of earnings resulting from the rapid loss of biodiversity. Physical risks are especially significant for business enterprises that rely on genetic resources from rare and extinction-threatened plants and animals for their activities, such as medicines, pharmaceuticals, and food production.Footnote 64 The rapid extinction of such genetic resources may disrupt production activities or may significantly raise transaction costs. On the other hand, transition risks may arise from the increased adoption of biodiversity and nature conservation policies across the MENA region, which may reduce the value or worth of assets or increase compliance costs. For example, ongoing global efforts to halt biodiversity loss may result in new standards that may fundamentally change business structures, limit the availability of funding for land-based investments and projects, raise the cost of debts, capital, and long-dated securities, or ultimately result in stranded assets.Footnote 65 These transition risks will need to be carefully considered by lawyers when giving advice, especially given the rapid evolution of biodiversity strategies and policies in the MENA region. Third, as countries adopt biodiversity and nature conservation legislation, business enterprises will have increased obligations to report on biodiversity and nature conservation efforts, as well as the financial impacts of biodiversity-related risks and opportunities on the business and its shareholders.

Legal risks relating to nondisclosure or greenwashing, which may result from misleading or inaccurate biodiversity disclosures, will need to be carefully considered by lawyers when providing advice. Furthermore, the likely impact of biodiversity-related risks and opportunities on the current and future financial position of a company as reflected in its income statement, cash flow statement, and balance sheet could play significant roles when negotiating asset values.Footnote 66 These and other obligations that may arise from emerging biodiversity law and policy must be carefully monitored and considered by lawyers as part of corporate due diligence and contract negotiation processes to prevent legal risks.

18.3 Conclusion

The rich and extensive natural capital of the MENA region play pivotal roles in supporting economic, social, and environmental development in key sectors. However, like many other world regions, the MENA region faces a rapid biodiversity loss emergency that requires dynamic legal innovation and response. Furthermore, there is growing evidence that efforts to halt biodiversity loss through nature-based solutions may result in land grabs, the inequitable allocation of benefits arising from genetic resources, displacements, and the inadequate participation of women and youth in decision-making processes. There is therefore an urgent need for nexus and integrated implementation of biodiversity and nature conservation programs to ensure coherence and address inconsistencies.

This book has developed a profile of the multifarious regulatory and institutional gaps that limit the coherent development and application of biodiversity law and policy at national levels. While the manifestations of these challenges may be escalating in some countries, there is a consistent and urgent need for all MENA countries to effectively mainstream biodiversity considerations into all aspects of development planning and decision-making. A starting point will be to develop clear and comprehensive legislation on biodiversity that clarifies the regulatory models and the roles of different agencies and institutions in the implementation of biodiversity and nature conservation programs. There is also a need to address legal and institutional gaps to biodiversity financing and nature-focused entrepreneurship. A supportive governance framework is required to stimulate private sector investment and participation in biodiversity and conservation programs.

Biodiversity mainstreaming should not be seen as a task for governments alone. Business enterprises, investors, lenders, insurance companies, and their lawyers alike all have prominent roles to play in integrating biodiversity considerations into business decision-making processes and planning. As biodiversity and nature conservation legislation and rules emerge, corporate actors can reduce the legal liabilities and risks arising from the direct and indirect impacts of their activities on lands, ecosystems, and cultural heritage by integrating biodiversity and nature considerations into business decision-making processes and planning.

The success, or otherwise, of integrating biodiversity considerations into planning and investment decisions will also depend on available capacity. There is an urgent need to bridge capacity gaps in the region through increased investment on biodiversity research and education. Higher education institutions have crucial roles to play in developing innovative programs to train and equip stakeholders with the advanced skills needed to integrate biodiversity considerations into their entire operations and value chains. National authorities and industry stakeholders should provide increased support for multistakeholder capacity development programs, such as those spearheaded by UNEP and ASSELLMU, to accelerate the effective implementation of the wide range of international environmental law instruments on nature conservation and biodiversity across the region.

Footnotes

15 Integrating Biodiversity into Environmental Impact Assessments Lessons from the EIA Process in the Tigris and Euphrates Basin

1 Republic of Turkey, Ministry of Industry and Technology, “Southeastern Anatolia Project” www.gap.gov.tr/en/what-s-gap-page-1.html accessed January 29, 2024.

2 Tehran Times, “Rouhani Opens Tropical Water Project in Kermanshah” (May 3, 2019) www.tehrantimes.com/news/435382/Rouhani-opens-tropical-water-project-in-Kermanshah accessed January 30, 2024.

3 C. J. Richardson and N. A. Hussain, “Restoring the Garden of Eden: An Ecological Assessment of the Marshes of Iraq” (2006) 56 BioScience 477.

4 The EIA is the process of identifying, predicting, evaluating, and managing the biophysical, social, health, and other relevant impacts of development proposals prior of taking any major decision and commitments. The EIA process includes consideration of all significant impacts, namely direct, indirect, and cumulative impacts. See: B. Sadler et al., Environmental and Social Impact Assessment for Large Scale Dams (World Commission on Dams Secretariat 2000).

5 Damilola Olawuyi, Environmental Law in Arab States (Oxford University Press 2022) 115118.

6 Footnote Ibid. See also Katalyn A. Voss, James S. Famiglietti, MinHui Lo, Caroline de Linage, Matthew Rodell, and Sean C. Swenson, “Groundwater Depletion in the Middle East from GRACE with Implications for Transboundary Water Management in the Tigris–Euphrates–Western Iran Region” (2013) 49 Water Resources Research 904.

7 Olawuyi (n 5) 115–119.

8 Mohamed Mostafa Mohamed and Samy Ismail Elmahdy, “Remote Sensing of the Grand Ethiopian Renaissance Dam: A Hazard and Environmental Impacts Assessment” (2017) 8 Geomatics, Natural Hazards and Risk 2, 1225.

10 C. Y. Keong, Global Environmental Sustainability Case Studies and Analysis of the United Nations’ Journey toward Sustainable Development (Elsevier, 2021) 63202.

11 Convention on Biological Diversity, 1760 UNTS 79, 31 ILM 818 (1992) (Date of Adoption, May 22, 1992; Place of Adoption, Rio de Janeiro).

13 L. S. Anderson, C. E. Davies, and D. Moss, “The UN Convention on Biological Diversity” (1997) 5.

14 Convention on Biological Diversity (June 5, 1992) 1760 UNTS 79, 143; 31 ILM 818 (1992), Article 14.

15 Footnote Ibid., Article 3.

16 Owen McIntyre, “The Current State of Development of the No Significant Harm Principle: How Far Have We Come?” (2020) 20 International Environmental Agreements: Politics, Law and Economics 601.

17 Stephen C. McCaffrey, Christina Leb, and Riley T. Denoon, Research Handbook on International Water Law (Edward Elgar Publishing 2019) 83.

18 Charles Harper, Charles L. Harper, and Monica Snowden, Environment and Society: Human Perspectives on Environmental Issues (Routledge 2017) 5253.

19 Madrid Declaration of the Institute for International Law on International Regulations regarding the Use of International Watercourses for Purposes Other than Navigation (1911).

20 Corfu Channel Case (United Kingdom v Albania) (Merits and Judgment) (1949) ICJ Rep 22.

21 United Nations Convention on the Law of the Non-navigational Uses of International Watercourses (May 21, 1997) 36 ILM 700 (International Watercourses Convention).

23 United Nations Economic Commission for Europe (UNECE), Convention on the Protection and Use of Transboundary Watercourses and International Lakes, 1992, UN Doc ECE/MP.WAT/41 (UNECE Water Convention).

24 Convention on Biological Diversity, Article 14.

25 UNECE, Convention on Environmental Impact Assessment in a Transboundary Context (Espoo Convention) (adopted February 1991, entered into force September 10, 1997) 1989 UNTS 309.

26 Footnote Ibid., Article 2(3).

27 Olawuyi (n 5) 124–125. See also Economic and Social Commission for Western Asia (ESCWA), “A Study on the Evaluation of Environmental Impact Assessment in Selected ESCWA Countries” (July 17, 2001) E/ ESCWA/ENR/2001/8;.

28 Nadhir Al-Ansari, “Hydro Geopolitics of the Tigris and Euphrates” in Recent Researches in Earth and Environmental Sciences: 2nd International Conference on Advanced Science and Engineering 2019 (ICOASE2019) Zakho-Duhok, Kurdistan Region – Iraq (Springer International Publishing 2019) 53.

29 Footnote Ibid., 60.

30 Katalyn A. Voss et al., “Groundwater Depletion in the Middle East from GRACE with Implications for Transboundary Water Management in the Tigris‐Euphrates‐Western Iran Region” (2013) 49 Water Resources Research 904.

32 Nadhir Al-Ansari et al., “Water Quality within the Tigris and Euphrates Catchments” (2018) 8 Journal of Earth Sciences and Geotechnical Engineering 95.

33 Aysegül Kibaroglu, “State-of-the-Art Review of Transboundary Water Governance in the Euphrates–Tigris River Basin” (2019) 35 International Journal of Water Resources Development 4, 9.

34 A. A. Al-Zubaidi, “The Importance of Geodiversity on the Animal Diversity in Huwaiza Marsh and the Adjacent Areas, Southeastern Iraq” (2017) 14 Bulletin of the Iraq Natural History Museum 235.

35 Itzchak E. Kornfeld, Mega-Dams and Indigenous Human Rights (Edward Elgar 2020) 126127.

36 United Nations Convention on the Law of the Non-navigational Uses of International Watercourses (May 21, 1997) 36 ILM 700 (International Watercourses Convention), also Qaraman Hasan, A Trans-national Analysis of Equitable Utilisation and Minimisation of Environmental Harm under Environmental Laws at International, Federal and National Levels (University of Waikato 2023) 222–223.

37 The marshlands of Iraq and the Relict Landscape of the Mesopotamian Cities is a mixed serial heritage property located in the southern region of the Republic of Iraq. The nominated property comprises seven components, four of which are natural with associated cultural value whereas the three other components are cultural. The natural components include the Huwaizah and the central, east, and west Hammar Marshes, while the cultural components comprise the archaeological cities of Uruk and Ur together with the Tell Eridu archaeological site. Republic of Iraq, “The Ahwar of Southern Iraq: Refuge of Biodiversity and the Relict Landscape of the Mesopotamian Cities” document prepared by the National Committee for the Environmental and Cultural Management of the Ahwar and their World Heritage Nomination (January 2014) 3.

38 GAP-RDA (Southeastern Anatolia Project – Regional Development Administration), “History of GAP” (October 24, 2022) www.gap.gov.tr/en/ accessed January 31, 2024. The construction of dams and irrigation tunnels was originally set to be completed by 2010, but this has now been delayed by several years, due to the funding problems that are directly related to Turkey’s dispute with Syria and Iraq over the rights to water resource, the World Bank has refused to provide loans because Turkey refused to comply with the international standards for such projects. See Joost Jongerden, “Dams and Politics in Turkey: Utilizing Water, Developing Conflict” (2010) 17 Middle East Policy 139.

39 Mohammed Al-Najim, “Impact of Tigris and Euphirates Water Crisis on the Environmental Catastrophe of Iraqi Marshlands” (2005) 34–38 Iraqi Geological Journal 96.

41 Laith Al-Oubedi and Dicle Tuba Kilic, Challenge C: Ecosystem Tigris-Euphrates River Ecosystem: A Status Report (Mesopotamian Water Forum 2019), 13.

42 According to the 2009 FAO report, there are approximately 6.5–7 million hectares of agricultural land in the Tigris–Euphrates basin that is being irrigated; the majority is Iraqi farmland, which covers about one-fifth of the country, and which is almost entirely dependent on irrigation from the Tigris and Euphrates Rivers. Only in the northeastern plains and mountain valleys is there rain-fed farming. Food and Agricultural Organization of the United Nations (FAO), Irrigation in the Middle East Region in Figurs-Aquastat Survey 2008 (FAO 2009).

43 Al-Najim (n 39) 96.

46 Frederick Lorenz and Edward Erickson, The Euphrates Triangle: Security Implications of the Southeast Anatolia Project (National Defense University Press 1999) 47.

47 Dana Muhammad Faraj, Kawa Z. Abdulrahman, and Nadhir A. Al-Ansari, “The Impact of the Tropical Water Project on the Operation of Darbandikhan Dam” (2022) 36 Journal of King Saud University-Engineering Sciences 6, 385.

48 FAO (n 42).

49 Kamal Chomani and Tune Bijee, The Impact of the Daryan Dam on the Kurdistan Region of Iraq (Save the Tigris and Iraqi Marshes Campaign 2016.

50 Ercan Ayboga, “Policy and Impacts of Dams in the Euphrates and Tigris Basin” paper for the Mesopotamia Water Forum (2019) Sulaymaniyah, Kurdistan Region of Iraq, 2.

51 Andrew Lawler, Reviving Iraq’s Wetlands (American Association for the Advancement of Science 2005).

52 Al-Najim (n 39) 95.

53 This recognition was initiated by the inclusion of the Huwaizah Marshes on the Ramsar List in 2006, under five criteria out of nine adopted for the agreement.

54 Lawler (n 51).

55 Sam Kubba, The Iraqi Marshlands and the Marsh Arabs: The Ma’dan, Their Culture and the Environment (Trans Pacific Press 2011).

57 Nadhir Al-Ansari, “Management of Water Resources in Iraq: Perspectives and Prognoses” (2013) 5 Engineering 8, 667.

60 Abdul Hameed M. Jawad Al Obaidy, “The Challenges of Water Sustainability in Iraq” (2013) 31 Engineering and Technical Journal 828.

61 Qaraman Hasan, Sarkawt Ghazi Salar, Durgeshree Raman, Sam Campbell, and Ibrahim Qasim Palani, “When the Law Is Unclear: Challenges and Opportunities for Data and Information Exchange in the Tigris–Euphrates and Indus River Basins” (2023) 8 Water Policy 25, 780.

62 Nadhir Al-Ansari and Sven Knutsson, “Toward Prudent Management of Water Resources in Iraq” (2011) 1 Journal of Advanced Science and Engineering Research 63.

64 Mesopotamia has a universally great cultural heritage and human history dating back 12,000 years when in the upper regions the first human settlements were established. Around 4000–3500 bc the first big civilizations were founded by the Sumerians.

65 The FAO delegate in Iraq reported that the flow of the country’s major rivers had decreased by about 40 percent. The “drop in water delivered downstream from dams constructed in the riparian state, Türkiye,” according to the FAO, was cited as a contributing factor in the decreased flow. FAO Representation in Iraq, Drought Situation in Iraq, Submitted to the UN SC661 Committee (May 28, 2000).

66 Al-Ansari et al. (n 31) 103.

67 V. Sissakian, N. Al-Ansari, and S. Knutsson, “Sand and Dust Storm Events in Iraq” (2013) 5 Journal of Natural Science 10, 1084.

68 For instance, research has shown that due to the WTP construction, about 48.4 percent of the power generation capacity of the Darbandikhan dam will be lost and the water surface elevation in the reservoir would be significantly affected. See Dana Mohammed Faraj et al., “The Impact of the Tropical Water Project on the Operation of Darbandikhan Dam” (2022)36 Journal of King Saud University - Engineering Sciences 6, 385.

69 Al Ansari and Knutsson (n 62).

70 Republic of Iraq, Ministry of Environment, “Sixth National Report to the Convention on Biodiversity” www.undp.org/iraq/publications/sixth-national-report-convention-biodiversity accessed January 31, 2024.

71 Al Ansari and Knutsson (n 62) 62.

72 Republic of Iraq, “Environmental Statistics for Iraq 2021” (Agricultural Indicators) A report by the Central Statical Organizations (CSO) (2022) https://cosit.gov.iq/ar/env-stat/envi-stat (in Arabic) accessed January 31, 2024.

73 H. Salmabadi and M. Saeedi, “A Real Fluctuations Monitoring of Al-Azim/Al-Havizeh Wetland during the 1986–2017 Period Using Time-Series Landsat Data” The Second International Conference on Strategic Ideas for Architecture Urbanism Geography and Environment (2018) Mashhad Iran.

74 Al-Najm (n 39) 99.

75 Al-Oubedi and Kilic (n 41) 13.

76 Nasrat Adamo, Nadhir Al-Ansari, and Varoujan Sissakian, “How Dams Can Affect Freshwater Issues in the Euphrates–Tigris Basins” (2020) 10 Journal of Earth Sciences and Geotechnical Engineering 43.

77 Karma el-Fadel Muatasem El-Fadel, “Comparative Assessment of the EIA in the MENA Countries Challenges and Prospects” (2004) 24 Environmental Impact Assessment Review 553.

78 Environment Law, Law No. 2872 of 1983, published in: 18132 Official Gazette of the Republic of Türkiye (August 11, 2008).

79 Environmental Protection and Enhancement Law of 1974, published in: 8592 Official Gazette (April 6, 1974).

80 Decree No. 225 of 2008 on Executive Procedures for Environmental Impact Assessment in the Syrian Arab Republic (Decree 225/2008).

81 Law for the Improvement and Protection of the Environment, Federal Law No. 27 of 2009, published in: 4142 Official Gazette of the Republic of Iraq (January 25, 2010).

82 Maggie Ronayane, The Cultural and Environmental Impacts of Large Dams in Southeast Türkiye, Fact Finding Mission Report (University of Ireland and Kurdish Human Rights Association February 2005) 5.

83 Fatemeh Khosravi, Urmila Jha-Thakur, and Thomas B Fischer, “The Role of the Environmental Assessment EA in the Iranian Water Management” (Environmental Assessment and Management Research Centre, School of Environmental Science, University of Liverpool 2018) 9.

84 Ronayane (n 82) 38.

85 Footnote Ibid. Also Olawuyi (n 5).

87 Khosravi et al. (n 83) 10.

88 Khosravi et al. (n 83) 13.

89 Laurel Northmore and Malcolm D. Hudson, “Digital Environmental Impact Assessment: An Exploration of Emerging Digital Approaches for Non-Technical Reports” (2022) 92 Environmental Impact Assessment Review 106689.

91 See Chapter 17.

16 Multistakeholder Participation in Biodiversity and Nature Conservation in the MENA Region

1 See Chapter 1. See also International Monetary Fund, Regional Economic Outlook: Middle East and Central Asia – Mounting Challenges, Decisive Times (IMF 2022) Statistical Appendix.

2 See Chapter 1.

3 Mina Devkota et al., “Conservation Agriculture in the Drylands of the Middle East and North Africa [MENA] Region: Past Trend, Current Opportunities, Challenges and Future Outlook” (2022) 172 Advances in Agronomy 253.

4 Damilola Olawuyi, Environmental Law in Arab States (Oxford University Press 2022) 105108.

6 Nafeesa Esmail, “What’s on the Horizon for Community-Based Conservation? Emerging Threats and Opportunities” (2023) 38 Trends in Ecology & Evolution 666.

8 Other interrelated concepts include multistakeholder engagement, multistakeholder dialogue, and multistakeholder partnership. Although these concepts have some variations, they are sometimes used interchangeably.

9 UN DESA, International Decade for Action, Water for Life (2015) UN-Water Annual International Zaragoza Conference www.un.org/waterforlifedecade/waterandsustainabledevelopment2015/multistakeholder_dialogue_17_01_2015.shtml accessed August 29, 2023.

10 After the Secretary-General of the UN called for the mainstreaming of human rights into all the works of the UN in 1997, various UN organizations met in 2003 to develop a Common Understanding on the Human Rights-Based Approach in response to the considerable changes in the international development community at that time. United Nations Office of the Human Rights High Commissioner, Statement by Mr. Kofi Annan, Secretary-General of the United Nations to the Opening of the Fifty-Fourth Session of the Commission on Human Rights (March 16, 1998) SG/SM/98/53; United Nations Sustainable Development Group, “The Human Rights Based Approach to Development Cooperation towards a Common Understanding Among UN Agencies” (2003) https://unsdg.un.org/resources/human-rights-based-approach-development-cooperation-towards-common-understanding-among-un accessed August 25, 2023.

12 As Amina Mohammed, Deputy Secretary-General of the UN observes, to achieve the 2030 Agenda for Sustainable Development and the seventeen Sustainable Development Goals (SDGs) and commitment to leave no one behind, “we need to ensure that we provide a voice and platforms for the meaningful participation and engagement of the most marginalized, vulnerable and excluded communities and individuals.” Amina Mohammed, “Participation, Consultation and Engagement: Critical Elements for an Effective Implementation of the 2030 Agenda” (2018) 2 UN 2030 Agenda 55.

13 The idea of participation has its theoretical root in the participatory development theory of international law. Many other theories can be brought to bear on participation; these include, multistakeholder theory (promotes the active involvement of different stakeholders in decision making), liberal democracy (promotes the principles that protect the rights of individuals as protected by law), civic republicanism (underscores the interconnection of individual freedom and civic participation for the common good), and deliberative democracy (which is a form of democracy in which deliberation is central to decision making). Participatory development theory, however, is remarkably important to the environmental and natural resource management discourse. George Pring and Susan Noé, “The Emerging International Law of Public Participation Affecting Global Mining, Energy, and Resources Development” in Donald Zillman, Alastair Lucas, and George Pring (eds), Human Rights in Natural Resource Development: Public Participation in the Sustainable Development of Mining and Energy Resources (Oxford University Press 2002) 13.

14 Karin Bäckstrand, “Multi-stakeholder Partnerships for Sustainable Development: Rethinking Legitimacy, Accountability and Effectiveness” (2006) 16 European Environment 290.

15 UNEP, Promoting Dialogue, Dams and Development Projects (Information Sheet No 4, DU/CP/3010-01-17/Rev, 2007).

16 See for example, Tasos Hovardas, “Social Sustainability as Social Learning: Insights from Multi-stakeholder Environmental Governance” (2021) 13 Sustainability 7744; Anne-Birgitte Albrectsen, Why Collaboration Will Be Key to Achieving the Sustainable Development Goals (World Economic Forum 2017); Giuseppe Ioppolo et al., “Sustainable Local Development and Environmental Governance: A Strategic Planning Experience” (2016) 8 Sustainability 180.

17 The legal basis for public participation is grounded in various international, regional, and national instruments. Notably, international human rights law recognizes the right of everyone to take part in public affairs that impact their interests. The Universal Declaration of Human Rights affirms everyone’s right to participate, directly or through their democratically elected representatives, in the governance of their state. Article 21, United Nations General Assembly, Universal Declaration of Human Rights (December 10, 1948, 217 A [III]). Article 25 of the International Covenant on Civil and Political Rights states that “every citizen shall have the right and opportunity to take part in the conduct of public affairs, directly or through freely chosen representatives,” International Covenant on Civil and Political Rights (December 16, 1966, Treaty Series, Vol. 999 at 171).

18 Convention on Access to Information, Public Participation in Decision-Making and Access to Justice in Environmental Matters (June 25, 1998, Treaty Series, Vol. 2161 at 447) (Aarhus Convention).

19 United Nations General Assembly, Protocol on Pollutant Release and Transfer Registers to the Convention on Access to Information, Public Participation in Decision-Making and Access to Justice in Environmental Matters (October 8, 2009, Treaty Series, Vol. 2626 at 119) (PRTRs).

20 Aarhus Convention (n 18) Preamble.

21 Aarhus Convention (n 18), Articles 6–8.

22 Article 1 of the Convention on Biological Diversity, United Nations, December 29, 1993, Treaty Series, Vol. 1760 at 79.

23 Footnote Ibid., Article 8(j).

24 Footnote Ibid., Article 14(1).

25 Article 23 of the Cartagena Protocol on Biosafety to the Convention on Biological Diversity (adopted January 29, 2000, entered into force September 11, 2003) 2226 UNTS 208.

26 The UNFCCC states that in order to actualize states’ commitments in the convention, states are required to provide access to information concerning climate change and its effects, create opportunities for public involvement in the process of addressing climate change and developing sufficient responses, and promote extensive public participation in the development of public awareness programs concerning climate change. Articles 4(1)(i) and 6(a) of United Nations Framework Convention on Climate Change, May 9, 1992, Treaty Series, Vol. 1771, 107.

27 The SCPOP underscores the responsibility of state parties to promote and implement measures to provide all available information to the public concerning persistent organic pollutants, to ensure public participation in addressing persistent organic pollutants, to provide opportunities for the public to provide input on the implementation of the convention, and to encourage public awareness about organic pollutants. Article 10(1) of Stockholm Convention on Persistent Organic Pollutants, May 17, 2004, Treaty Series, Vol. 2256 at 119.

28 The UNCCD “gives new recognition to the essential roles of both village-level and NGO participation in policy planning and implementation.” The convention affirms the duty of states to facilitate public participation and promote awareness in the attempt to combat desertification and mitigate the consequences of drought. Article 5 of United Nations Convention to Combat Desertification in those Countries Experiencing Serious Drought and/or Desertification, Particularly in Africa, December 26, 1996, Treaty Series, Vol. 1954 at 3.

29 For instance, parties to the United Nations Framework Convention on Climate Change commented that climate adaptation actions should be in accordance with a “participatory and fully transparent approach, taking into consideration vulnerable groups, communities and ecosystems.” Paragraph 12, UNFCCC, Report of the Conference of the Parties on its Sixteenth Session, held in Cancun from November 29 to December 10, 2010 (FCCC/CP/2010/7/Add.1, March 15, 2011).

30 For example, see Principles 10, 20–22 of The Rio Declaration on Environment and Development (August 12, 1992) The United Nations Conference on Environment and Development, A/CONF.151/26 [Vol. I].

31 Toktakunov v Kyrgyzstan (2011) UN Human Rights Committee, CCPR/C/101/D/1470/2006, para 6.3.

32 Organization for Economic Co-operation and Development, “Recommendation of the Council on Open Government” (December 14, 2017) C[2017]140-C/M [2017]22 at para 7.

33 Principle 10, United Nations Economic and Social Council, Rio Declaration on Environment and Development: Application and Implementation (April 1997) 5th session of the Commission on Sustainable Development E/CN.17/1997/8.

34 Footnote Ibid., Article 7.

35 Aarhus Convention (n 18) Article 7. Judicial precedents also emphasize the principles ingrained in the Aarhus Convention. For related case law on the Aarhus Convention, see the UN compilation. United Nations Economic Commission for Europe, “Case Law Related to the Convention” (2021) https://unece.org/environment-policy/public-participation/tfaj/case-law-related-convention accessed August 15, 2023.

36 PRTRs (n 21) Article 1.

37 Jeroen F. Warner, “More Sustainable Participation? Multi-stakeholder Platforms for Integrated Catchment Management” (2006) 22 International Journal of Water Resources Development 15, 21.

38 Amy Gutmann and Dennis Thompson, “Why Deliberative Democracy?” (Princeton University Press 2004) 4.

39 See Janette Hartz-Karp and Dora Marinova, “Using Deliberative Democracy for Better Urban Decision-Making through Integrative Thinking” (2020) 5 Urban Science 3.

40 Het Onderscheid, “What Characterizes a Strategic Shareholder Dialogue?” in Rob Van Tulder et al. (eds), The Strategic Stakeholder Dialogue (English translation by Lewis Van Leeuwen, Erasmus University Rotterdam and Schuttelaar & Partners 2004) 29.

41 Olawuyi (n 4).

43 United Nations Treaty Collection: Status of Treaties, Convention of Biological Diversity [status as at December 7, 2023] https://treaties.un.org/Pages/ViewDetails.aspx?src=TREATY&mtdsg_no=XXVII-8&chapter=27&clang=_en accessed December 4, 2023; United Nations Treaty Collection: Status of Treaties, Cartagena Protocol on Biosafety to the Convention on Biological Diversity [status as at December 7, 2023].

44 Nagoya Protocol on Access to Genetic Resources and the Fair and Equitable Sharing of Benefits Arising from Their Utilization to the Convention on Biological Diversity entered into force October 12, 2014, 3008 United Nations Treaty Series, 3.

45 The Kingdom of Bahrain Supreme Council for Environment, “Fifth National Report to the Convention on Biological Diversity” (January 2016) UNEP 38.

46 Arab Republic of Egypt, Ministry of Environment, “Egyptian Biodiversity Strategy and Action Plan, 2015–2030” (January 2016) www.cbd.int/doc/world/eg/eg-nbsap-v2-en.pdf accessed December 3, 2023.

47 United Nations Department of Economic and Social Affairs, Sustainable Development: The 17 Goals https://sdgs.un.org/goals accessed December 2, 2023. Only SDGs 14 and 15 specifically refer to biodiversity, but biodiversity loss has significant impacts on the fulfillment of other goals including access to food and clean water, health and well-being, and gender equality. Malgorzata Blicharska et al., “Biodiversity’s Contributions to Sustainable Development” (2019) 2 Nature Sustainability 1083.

48 National Committee on Sustainable Development Goals, “UAE and the 2030 Agenda for Sustainable Development: Excellence in Implementation” (2017) https://sustainabledevelopment.un.org/content/documents/20161UAE_SDGs_Report_Full_English.pdf accessed December 2, 2023.

49 The three identified stakeholders are youths, private sector, and academic institutions. Footnote Ibid., 31–34.

50 Footnote Ibid., 120–124.

51 Islamic Republic of Iran, Department of Environment, Deputy for Natural Environment and Biodiversity, Revised National Biodiversity Strategies and Action Plan (NBSAP2) 2016–2030.

52 Footnote Ibid., 22.

53 Footnote Ibid., 31–32.

54 Biosafety of Genetically Modified Organisms (United Arab Emirates Federal Law No. [9] of 2020) (UAE Biosafety Law).

55 Article 2 of the Qatar Environmental Protection Law (Resolution No. 4 of 2005 by the Chairperson of the Supreme Council of the Environment and Natural Reserves [SCENR]) (Qatar EPL); Article 5[3] of Kingdom of Saudi Arabia Executive Regulation for the Protected Areas for the Environmental Law (issued by Royal Decree No [m/165], 19/11/1441 Hijri) [Saudi Arabia Environmental Law].

56 See for example Articles 19–24 of UAE Biosafety Law, Articles 66–75 of Qatar EPL, Article 10 of Saudi Arabia Environmental Law.

57 Anna-Kaisa Tupala, Suvi Huttunen and Panu Halme, “Social Impacts of Biodiversity Offsetting: A Review” (2022) 267 Biological Conservation 10943.

58 United Arab Emirates, “Information and Services: Ministry of Climate Change and Environment” www.moccae.gov.ae/en/about-ministry/about-the-ministry/strategic-goals.aspx accessed December 4, 2023.

59 The Justice, Safety and the Law Department’s web page provides a list of services they provide including environmental protection, but the section on environmental protection redirects to the Ministry of Climate Change and Environment page. United Arab Emirates, “Information and Services: Justice, Safety and the Law” https://u.ae/en/information-and-services/justice-safety-and-the-law accessed December 4, 2023.

60 Qatar Ministry of Environment, National Biodiversity Strategy and Action Plan 2015–2025 (2014).

61 Holger Hoff et al., “A Nexus Approach for the MENA Region: From Concept to Knowledge to Action” (2019) 7 Frontiers in Environmental Science 48, 1. See also Damilola Olawuyi, “Sustainable Development and the Water–Energy–Food Nexus: Legal Challenges and Emerging Solutions” (2020) 103 Journal of Environmental Science and Policy 1.

62 CBD Convention of the Parties Decisions, Contribution from the Conference of the Parties to the Convention on Biological Diversity to the World Summit on Sustainable Development: Annex to The Hague Ministerial Declaration of the Conference of the Parties to the Convention on Biological Diversity (COP6 Decision VI/21) paras 10–11.

63 See Chapter 6. See also Neil Dawson et al., “The Role of Indigenous Peoples and Local Communities in Effective and Equitable Conservation” (2021) 26 Ecology and Society 19.

64 Hoff et al. (n 61).

65 Footnote Ibid. See also H. Jowkar et al., “The Conservation of Biodiversity in Iran: Threats, Challenges and Hopes” (2016) 49 Iranian Studies 6, 1065.

66 Footnote Ibid., Article 8(j).

67 See Chapter 10.

68 The World Bank, “MENA: Global Action Is Urgently Needed to Reverse Damaging Jumps in Extreme Poverty” press release (October 2020).

70 See Chapter 10.

71 Samantha Miles, “Stakeholder Theory Classification: A Theoretical and Empirical Evaluation of Definitions” (2015) 142 Journal of Business Ethics 437.

72 Mark S. Reed et al., “Who’s in and Why? A Typology of Stakeholder Analysis Methods for Natural Resource Management” (2009) 90 Journal of Environmental Management 1933.

73 United Nations Environmental Programme, Overview of Stakeholder Engagement Frameworks under other Instruments and of Potential Approaches for the International Legally Binding Instrument on Plastic Pollution, including in the Marine Environment (Note by the Secretariat, UNEP/PP/INC.1/12, September 9, 2022) 2.

74 For a conceptual analysis of stakeholders in environmental decision-making, see Neal Haddaway et al., “A Framework for Stakeholder Engagement during Systemic Reviews and Maps in Environmental Management” (2017) 6 Environmental Evidence 1.

75 United Nations Development Programme, Climate Change Adaptation in the Arab States: Best Practices and Lessons Learned (UNDP 2018).

76 Article 6 of the CBD.

77 CBD Subsidiary Body on Implementation, Update on Progress in Revising/Updating and Implementing National Biodiversity Strategies and Action Plans, including National Targets (2018) cbd.int/doc/c/fcae/4aa8/dd3362074b26490c60880abd/sbi-02-02-add1-en.pdf accessed December 8, 2023.

78 Simo Sarkki et al., “Are National Biodiversity Strategies and Action Plans Appropriate for Building Responsibilities for Mainstreaming Biodiversity across Policy Sectors? The Case of Finland” (2016) 59 Journal of Environmental Planning and Management 1377.

79 Riyad Fakhri, Laila Dalaa, and Saad Belkasmi, “Enhancing the Effectiveness of National and Regional Institutions in Addressing Climate Change in the MENA Region” in Damilola Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2022) 111112.

80 Office of the United Nations High Commissioner for Human Rights, “Human Rights-Based Approaches to Conserving Biodiversity: Equitable, Effective and Imperative: A Policy Brief from the UN Special Rapporteur on Human Rights and the Environment, David R Boyd and Stephanie Keene” Policy Brief No 1 (August 2021) 3.

81 Marya Axner, “Promoting Coordination, Cooperative Agreements, and Collaborative Agreements among Agencies” https://ctb.ku.edu/en/table-of-contents/implement/improving-services/coordination-cooperation-collaboration/main accessed February 11, 2024.

17 Strengthening the Implementation of Biodiversity Treaties through Environmental Law Education

1 Generally, see Malgosia Fitzmaurice, Meagan S. Wong, and Joseph Crampin, International Environmental Law: Text, Cases and Materials (Edward Elgar 2022).

2 There are diverse conceptualizations or understandings of which countries are part of the MENA region. This chapter adopts the categorization enunciated in Chapter 1.

3 Gazliya Nazimudheen, “Things to Know about Habitat Loss in MENA” (EcoMENA, August 24, 2022) www.ecomena.org/habitat-loss-in-mena/ accessed October 15, 2023.

4 Damilola S. Olawuyi, Environmental Law in Arab States (Oxford University Press 2022) 248260.

5 The IUCN Red List of Threatened Species www.iucnredlist.org/ accessed October 15, 2023.

6 Generally, see Rajaa El Kassab, “A Region in Danger! Biodiversity in the Arab Region” (Policy Commons, August 15, 2022) https://policycommons.net/artifacts/2654130/a-region-in-danger-biodiversity/3677034/ accessed October 15, 2023.

8 Critical Ecosystem Partnership Fund, “Biodiversity Hotspots Defined” www.cepf.net/our-work/biodiversity-hotspots/hotspots-defined accessed October 15, 2023.

9 Kira Walker, “MENA’s Biodiversity Shrinking under the Pressure of Climate Change” (Nature Middle East December 13, 2022) www.natureasia.com/en/nmiddleeast/article/10.1038/nmiddleeast.2022.79#:~:text=The%20rich%20biodiversity%20found%20in,and%20animal%20resources%3B%20and%20pollution accessed October 15, 2023.

11 Generally, see Olawuyi (n 4).

12 Phillipe Sands and Jacqueline Peel, Principles of International Environmental Law (4th ed., Cambridge University Press 2018) 385.

13 Fatima Eshun et al., “A Survey of the Role of Environmental Education in Biodiversity Conservation in the Greater Accra Region of Ghana” (2022) 2 Conservation 2, 297, 298.

14 Generally, see Osamuyimen Enabulele and Eghosa O. Ekhator, “Improving Environmental Protection in Nigeria: A Reassessment of the Role of Informal Institutions” (2022) 13 JSDLP 1, 162.

15 ASSELLMU, Training Manual for the Train-the-Trainers (TTT) Program in Environmental Law for Higher Education Institutions in the MENA Region (August 2021) 21 www.hbku.edu.qa/sites/default/files/train-the-trainers_eng.pdf accessed October 15, 2023.

17 Footnote Ibid., 20.

18 Generally, see Enabulele and Ekhator (n 14).

19 Generally, see Sufyan Droubi et al., “Transforming Education for the Just Transition” (2023) 100 Energy Research & Social Science 202103090.

20 UNESCO, “Education and Awareness” www.unesco.org/en/biodiversity/education accessed September 17, 2023.

21 Generally, see Najib Saab, Adan Badran, and Abdul-Karim Sadik, “Environmental Education for Sustainable Development in Arab Countries’ Annual Report of Arab Forum for Environment and Development” (AFED 2019) 1 www.afedonline.org/en/reports/details/environmental-education-for-sustainable-development-in-arab-countries accessed October 15, 2023.

23 Generally, see Afe Babalola and Damilola S. Olawuyi, “Advancing Environmental Education for Sustainable Development in Higher Education in Nigeria: Current Challenges and Future Directions” (2021) 13 Sustainability 19, 10808.

24 Generally, see Elizabeth M. Mrema and Aphrodite Smagadi, “The United Nations Environment Programme: Promoting Climate Law Education in the Middle East and North Africa” in Damilola S. Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2022).

25 Also, see Babalola and Olawuyi (n 23).

26 UNESCO, “Education for Sustainable Development: Towards Achieving the SDGs (ESD for 2030) and Its Roadmap for Implementation from 2020–2030” https://unesdoc.unesco.org/ark:/48223/pf0000370215.locale=en accessed October 17, 2023.

27 League of Arab States, “The Sustainable Development Initiative in the Arab Region” www.un.org/esa/sustdev/partnerships/activities_initiate/101202_sd_initiative_arab_region.pdf accessed February 12, 2024.

28 Law No 30 of 2002 Promulgating the Law of the Environment Protection 30/2002 www.fao.org/faolex/results/details/en/c/LEX-FAOC055012/ accessed February 12, 2024.

29 Qatar National Development Strategy 2011–2016; General Secretariat for Development Planning: Doha, Qatar, 2011. Also cited in Babalola and Olawuyi (n 23) 13.

30 United Arab Emirates, National Environmental Education and Awareness Strategy (2021) www.moccae.gov.ae/assets/b4a14e05/national-environmental-education-and-awareness-strategy-2015-2021-en.aspx accessed October 17, 2023.

31 Generally, see Mrema and Smagadi (n 24).

32 Generally, see Saab et al. (n 21). However, for contrary views, see Mrema and Smagadi (n 24).

33 Generally, see Train-the-Trainers (n 15); Saab et al. (n 21).

34 Train-the-Trainers (n 15) 20.

35 Train-the-Trainers (n 15); Mrema and Smagadi (n 24).

36 Generally, see Stuart Bell et al., Environmental Law (9th ed., Oxford University Press 2017).

37 Train-the-Trainers (n 15) 21.

38 Footnote Ibid., 21–22.

39 Also, see Kim Bouwer et al., “Climate Change Isn’t Optional: Climate Change in the Core Law Curriculum” (2023) 43 Legal Studies 2, 240.

40 Generally, see Footnote ibid.

41 Generally, see Mrema and Smagadi (n 24).

42 Mrema and Smagadi (n 24); Rob Fowler et al., “From ‘Marginality’ to ‘Mainstream’: The Evolution of Teaching and Learning in Environmental Law” in Amanda Kennedy et al. (eds), Teaching and Learning in Environmental Law: Pedagogy, Methodology and Best Practice (Edward Elgar, 2021); Bouwer et al. (n 39).

43 Olawuyi (n 4); Mrema and Smagadi (n 24).

44 Olawuyi (n 4) 4.

45 Generally, see Olawuyi (n 4); Mrema and Smagadi (n 24).

46 Generally, see Bouwer et al. (n 39).

47 Fowler et al. (n 42).

48 Generally, see Fowler et al. (n 42); Steven Vaughan et al., “Of Density and Decline: Reflections on Environmental Law Teaching in the UK and on the Co-production of Environmental Law Scholarship” in Amanda Kennedy et al. (eds), Teaching and Learning in Environmental Law: Pedagogy, Methodology and Best Practice (Edward Elgar 2021).

49 Generally, see Vaughan (n 48).

50 Generally, see Footnote ibid.

51 For some of the suggestions, see Bouwer et al. (n 39).

52 Generally, see Bouwer et al. (n 39). Also, see Tolulope N. Ogboru, “Environmental Education: Moving Environmental Law from Marginality to Mainstream3 International Journal of Law and Clinical Legal Education 83.

53 Train-the-Trainers (TTT) (n 15) 3.

54 Generally, see Mrema and Smagadi (n 24).

55 Saab et al. (n 21).

59 Footnote Ibid., 75.

60 Train-the-Trainers (n 15).

62 Footnote Ibid., 18.

63 Generally, see Walker (n 9).

64 Eshun (n 13) 297.

65 Olawuyi (n 4) 30. On the other hand, scholars including Joseph A. Omojolaibi and Solomon P. Nathaniel, “Assessing the Potency of Environmental Regulation in Maintaining Environmental Sustainability in MENA Countries: An Advanced Panel Data Estimation” (2022) 22 Journal of Public Affairs 3, e2526, have argued that environmental laws and regulations do not successfully improve environmental sustainability in the MENA region.

66 CBD Website, “List of Parties” www.cbd.int/information/parties.shtml accessed October 15, 2023.

67 CBD Website, “Country Profile: Jordan-Main Details” www.cbd.int/countries/profile/?country=jo accessed October 15, 2023.

68 Generally, see United Arab Emirates Ministry of Climate Change and Environment www.moccae.gov.ae/en/knowledge-and-statistics/biodiversity.aspx accessed October 15, 2023.

69 Fowler et al. (n 42) 8.

70 Olawuyi (n 4); Train-the-Trainers (n 15); Saab et al. (n 21).

71 Generally, see Alicia Santiago, “Enviro Law in Egypt: Egypt’s Only Public Interest Environmental Lawyer Visits Eugene” (Eugene Weekly, June 29, 2023) https://eugeneweekly.com/2023/06/29/enviro-law-in-egypt/#:~:text=Unlike%20the%20U.S.%2C%20Egypt%20lacks,their%20country%27s%20issues%2C%20Elseidi%20says accessed October 15, 2023.

72 Generally, see Olawuyi (n 4) 30.

73 Generally, see Hilary C. Bell, “Tackling the Legally Disruptive Problem of Climate Change with Disruptive Legal Education” in Damilola Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2021).

74 Also, see Footnote ibid.

75 Footnote Ibid., 258.

76 Damilola S. Olawuyi, “Conference Highlights Need to Introduce Environmental Law to Higher Education Curricula in the Middle East” (IUCN, November 28, 2018) www.iucn.org/news/world-commission-environmental-law/201811/conference-highlights-need-introduce-environmental-law-higher-education-curricula-middle-east accessed October 15, 2023. However, in recent times there have been specialist books published on the nature and content of environmental law by some leading including scholars in the MENA region. See for example, Damilola Olawuyi, Environmental Law in Arab States (Oxford University Press 2022); Damilola Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2021); Samira Idllalène, Rediscovery and Revival in Islamic Environmental Law (Cambridge University Press 2021).

77 However, see Max Roser and Esteban Ortiz-Ospina, Financing Education (Our World in Data 2016).

78 Generally, see Zainab Lokhandwala, “The Fallout of Covid-19 on Environmental Law in the Middle East and North Africa” (2020) Opinio Juris in Comparatione.

79 Generally, see Bell (n 73).

80 Generally, see Footnote ibid.

81 Generally, Saab et al. (n 21).

82 Generally, see World Bank, “Sustainable Land Management and Restoration in the Middle East and North Africa Region: Issues, Challenges, and Recommendations” (2019) https://elibrary.worldbank.org/doi/abs/10.1596/33037 accessed October 15, 2023.

83 Hadi B. Heidarlou et al., “Armed Conflict and Land-Use Changes: Insights from Iraq–Iran War in Zagros Forests” (2020) 118 Forest Policy and Economics 102246.

84 Beatriz DeQuero-Navarro et al., “From Conflict to Cooperation: A Macromarketing View of Sustainable and Inclusive Development in Lebanon and the Middle East” (2020) 66 Environmental Management 2, 232.

85 Generally, see Bell (n 73) and Saab (n 21).

86 Bell (n 73).

87 Walker (n 9).

88 Generally, see Walker (n 9).

89 Houman Jowkar et al., “The Conservation of Biodiversity in Iran: Threats, Challenges and Hopes” (2016) 49 Iranian Studies 6, 1065.

90 Also, see Olawuyi (n 2) 12.

91 PwC Middle East, “Nature and Biodiversity: Creating a Nature Positive Future” (2023) www.pwc.com/m1/en/publications/nature-biodiversity.html accessed October 15, 2023.

92 Generally, see the United Arab Emirates Ministry of Climate Change and Environment, “A Guide to Biodiversity Conservation in the UAE” (May 2023).

93 Footnote Ibid. Also, see the Convention on Biological Diversity (CBD) website, “United Arab Emirates – Main Details” www.cbd.int/countries/profile/?country=ae#:~:text=In%20addition%2C%20the%20UAE%20has,by%20%E2%80%9CEmirates%20vision%202021%E2%80%9D accessed October 15, 2023.

94 United Arab Emirates Ministry of Climate Change and Environment, “Biodiversity” www.moccae.gov.ae/en/knowledge-and-statistics/biodiversity.aspx accessed October 15, 2023.

95 Generally, see Fowler et al. (n 42).

96 Amanda Kennedy et al. (eds), Teaching and Learning in Environmental Law: Pedagogy, Methodology and Best Practice (Edward Elgar 2021).

97 Fowler et al. (n 42) 11.

98 Saab et al. (n 21) 13.

99 Kim Bouwer “Climate Consciousness in Daily Legal Practice” (Journal of Environmental Law Blog, May 22, 2015) https://blog.oup.com/2015/05/climate-consciousness-daily-legal-practice/?utm_source=feedblitz&utm_medium=FeedBlitzRss&utm_campaign=oupblog accessed October 15, 2023; Brian Preston, “Climate Conscious Lawyering: Implementing a Climate Conscious Approach in Daily Legal Practice” (2021) 95 Australian Law Journal 51.

100 Preston (n 99) 51.

101 Generally, see Droubi (n 19).

102 Droubi (n 19) 7.

103 Generally, see Bouwer (n 99) for analysis of the utility of a climate consciousness approach from a UK perspective.

104 Karen Hulme, “Using International Environmental Law to Enhance Biodiversity and Nature Conservation during armed conflict” (2022) 20 Journal of International Criminal Justice 5, 1155, 1173. Also, Hulme states that Article 12 and 13(a) CBD; Article 3(3) Bern Convention; Article 5(e), 22(c), 23, 27–28 WHC; and Article 4(5) Ramsar Convention provide for environmental education in their provisions.

105 Generally, see Articles 27 and 28 of the WHC which focuses on environmental education. Furthermore, the recognition of education as a strategy to enhance knowledge and awareness about biodiversity is explicitly acknowledged by the CBD.

106 Generally, see Hulme (n 104).

107 Warren G. Lavey, “Toolkit for Integrating Climate Change into Ten High-Enrollment Law School Courses” (2019) 49 Environmental Law 513.

108 Footnote Ibid., 515–516.

109 UNESCO, “Biodiversity: Education and Awareness” (December 20, 2022). www.unesco.org/en/biodiversity/education accessed October 15, 2023.

110 SDG Resources for Educators – Life on Land https://en.unesco.org/themes/education/sdgs/material/15 accessed October 15, 2023. Furthermore, this resource further states that “[b]iodiversity education contributes to integrating protective ecosystem and biodiversity values into national and local planning, development processes, poverty reduction strategies and accounts.”

111 Damilola S. Olawuyi, “Conference Highlights Need to Introduce Environmental Law to Higher Education Curricula in the Middle East” (IUCN, November 28, 2018) www.iucn.org/news/world-commission-environmental-law/201811/conference-highlights-need-introduce-environmental-law-higher-education-curricula-middle-east accessed February 12, 2024.

112 Generally, Mrema and Smagadi (n 24).

113 Mrema and Smagadi (n 24) 30.

114 Generally, see Fowler et al. (n 42).

115 ASSELLMU website, “About Us” https://assellmu.org/about-us/ accessed October 15, 2023.

117 Train-the-Trainers (n 15).

119 Generally, see Saab et al. (n 21).

120 Footnote Ibid., 9.

121 Generally, see Bell (n 73).

122 Bell (n 73) 258.

123 Also, see Bell (n 73) for similar allusions in the context of climate change education in MENA countries.

124 Rhuks Ako and Eghosa O. Ekhator, “The Civil Society and the Regulation of the Extractive Industry in Nigeria” (2016) 7 Journal of Sustainable Development Law and Policy 1, 183.

125 See, Pedi Obani and Eghosa Ekhator, “Transnational Litigation and Climate Change in Nigeria” in Symposium: Nigeria and International Law: Past, Present and the Future (AfronomicsLaw Blog 2021) www.afronomicslaw.org/category/analysis/transnational-litigation-and-climate-change-nigeria accessed October 15, 2023.

126 Generally, see Guillaume Futhazar, Sandrine Maljean-Dubois, and Jona Razzaque (eds), Biodiversity Litigation (Oxford University Press 2022).

127 Generally, see Clyde & Co website, “Biodiversity litigation: Environment Analysis” (April 12, 2022) www.clydeco.com/en/insights/2022/04/biodiversity-litigation-environment-analysis accessed October 15, 2023.

128 Futhazar et al. (n 126) 15.

129 Boya Jiang, “10 Landmark Cases for Biodiversity” (ClientEarth China, October 11, 2021) www.clientearth.org/latest/documents/10-landmark-cases-for-biodiversity/ accessed October 15, 2023.

130 Generally, see Ako and Ekhator (n 124).

132 Also, see Rob Fowler, “The Role of the IUCN Academy of Environmental Law in Promoting the Teaching of Environmental Law” (2017) 8 IUCNAEL e-Journal www.iucnael.org/en/academy-journal/previous-issues/86-journal/issue/640-issue-2017 accessed October 15, 2023.

18 Advancing the Nexus Approach to Biodiversity and Nature Conservation in the MENA Region Summary and Options for Policymakers

1 J. Richardson et al., “Earth beyond Six of Nine Planetary Boundaries” (2023) 9 Science Advances 37. See also W. Steffen et al., “Planetary Boundaries: Guiding Human Development on a Changing Planet” (2015) 347 Science 736.

2 See Chapter 1. See also Taskforce on Nature-related Financial Disclosures (TNFD), “Recommendations of the Taskforce on Nature-related Financial Disclosures” (September 2023) stating that nature and biodiversity loss “poses risks for businesses, capital providers, financial systems and economies, and that these risks are increasing in severity and frequency.” https://tnfd.global/wp-content/uploads/2023/08/Recommendations_of_the_Taskforce_on_Nature-related_Financial_Disclosures_September_2023.pdf?v=1695118661 accessed January 12, 2024.

3 See Chapters 1 and 514.

4 Convention on Biological Diversity (CBD), “Mainstreaming Biodiversity in Development Cooperation” (April 26, 2019) www.cbd.int/development/about/mainstreaming.shtml#:~:text=The%20mainstreaming%20of%20biodiversity%20can,or%20governments%20lead%20the%20process accessed January 12, 2024.

5 Convention on Biological Diversity, “Strategic Actions to Enhance the Implementation of the Strategic Plan for Biodiversity 2011–2020 and the Achievement of the Aichi Biodiversity Targets, Including with Respect to Mainstreaming and the Integration of Biodiversity Within and Across Sectors” CBD/COP/DEC/XIII/3 (December 16, 2016) para 2.

6 See Chapter 14. See also UNESCO, “World Heritage and Biodiversity” https://whc.unesco.org/en/biodiversity/#:~:text=Around%2020%25%20of%20UNESCO%20cultural,of%20land%2Duse%20that%20enhance accessed January 12, 2024.

7 See Chapter 5.

8 FoodPrint, “Biodiversity and Agriculture” (published: February 17, 2021; last updated: January 18, 2024) https://foodprint.org/issues/biodiversity-and-agriculture. See also Suchismita Mondal et al. “Harnessing Diversity in Wheat to Enhance Grain Yield, Climate Resilience, Disease and Insect Pest Resistance and Nutrition through Conventional and Modern Breeding Approaches7 Frontiers in Plant Science (July 6, 2016) www.frontiersin.org/articles/10.3389/fpls.2016.00991/full accessed January 25, 2024.

9 Convention on Biological Diversity, “National Biodiversity Strategies and Action Plans (NBSAPs)” (CBD.int) www.cbd.int/nbsap/ accessed January 15, 2023.

10 See Chapter 2. See also Convention on Biological Diversity, “Actions to Enhance Implementation of the Strategic Plan for Biodiversity 2011–2020” (May 11, 2018) www.cbd.int/sp/actions.shtml accessed January 16, 2023.

11 See Chapter 3. See also Samer Fakhoury and Reem AlHaddadin, “Conservation of Oasis Ecosystems in the MENA Region under Water Stress” (August 2023) www.kas.de/documents/264147/264196/Conservation+of+Oasis+Ecosystems+in+the+MENA+Region+under+Water+Stress.pdf/7b28c843-daac-d33e-8f13-b2fb65224232?version=1.1&t=1692805264626 accessed January 16, 2023.

12 See Chapters 6 and 7.

13 Damilola Olawuyi, “Sustainable Development and the Water–Energy–Food Nexus: Legal Challenges and Emerging Solutions” (2020) 103 Journal of Environmental Science and Policy 1.

14 CBD (n 5). See also CBD, “Guidelines for the Fifth Annual Report” www.cbd.int/doc/nr/nr-05/NR5-guidelines-en.pdf accessed January 12, 2024.

15 CBD (n 5), also, for detailed discussion of the concept of biodiversity-proofing, see M. Kettunen, K. Medarova-Bergstrom, M. Rayment, I. Shinner, and G. Tucker, “Common Framework for Biodiversity-Proofing of the EU Budget: Guidance for Cohesion Policy Funds” Report to the European Commission, Institute for European Environmental Policy, London (2014) http://minisites.ieep.eu/assets/1422/cfbp_-_Cohesion_funds.pdf accessed January 25, 2024.

16 See CBD, “Global Biodiversity Outlook 3: Towards a Strategy for Reducing Biodiversity Loss” www.cbd.int/gbo3/?pub=6667&section=6716 accessed January 12, 2024.

17 See Organisation for Economic Co-operation and Development, Scaling up Finance Mechanisms for Biodiversity (2013) chapter 3.

18 See TNFD (n 2) 97–98.

19 Footnote Ibid. See also Jennifer Bell, “How the Arabian Oryx Was Brought Back from Extinction” (Arab News, January 11, 2019).

20 TNFD (n 2) 97–98.

21 See Intergovernmental Panel on Climate Change, “Land Degradation” in P. R. Shukla et al. (eds), Climate Change and Land: An IPCC Special Report on Climate Change, Desertification, Land Degradation, Sustainable Land Management, Food Security, and Greenhouse Gas Fluxes in Terrestrial Ecosystems (IPCC nd) www.ipcc.ch/srccl/cite-report/ accessed January 12, 2024. See also P. Newton et al., “What Is Regenerative Agriculture? A Review of Scholar and Practitioner Definitions Based on Processes and Outcomes” (2020) 4 Frontiers in Sustainable Food Systems 577723.

22 CBD (n 14). See also Chapter 15.

23 See Chapter 10.

24 G. Dimitropoulos and A. Lokhandwala, “Addressing Climate Change in the MENA Region through Regulatory Design: Instrument Choice Questions” in D. Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2022) 6568.

25 Swiss Academy of Sciences, “Agreement on Access and Benefit Sharing for Non-commercial Research: Sector Specific Approach Containing Model Clauses” (2010) www.cbd.int/abs/doc/model-clauses/noncommresearch-abs-agreement.pdf accessed January 25, 2024.

26 The Chancery Lane Project, “New Land and Agriculture Clauses” https://chancerylaneproject.org/news/new-land-agriculture-clauses/ accessed August 27, 2023.

27 See Chapter 4.

28 See Chapter 16.

30 See D. Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2022) 110.

31 CBD (n 4).

32 See Chapter 10.

33 Thomas Daum, Frédéric Baudron, Regina Birner, Matin Qaim, and Ingo Grass, “Addressing Agricultural Labour Issues Is Key to Biodiversity-Smart Farming” (2023) 284 Biological Conservation 110165.

34 See Chapter 11.

35 See D. Olawuyi, “Can MENA Extractive Industries Support the Global Energy Transition? Current Opportunities and Future Directions” (2020) 8 Extractive Industries and Society Journal 2, 100685.

36 QNA, “Katara Unveils Establishment of Biodiversity Genome Program” www.qna.org.qa/en/News-Area/News/2023-09/02/0019-katara-unveils-establishment-of-biodiversity-genome-program accessed January 12, 2024.

37 Doha News, “Qatar’s Environmental Initiatives: Workshop Unveils Conservation Successes and Commitments” (January 1, 2024) https://dohanews.co/qatars-environmental-initiatives-workshop-unveils-conservation-successes-and-commitments/ accessed January 12, 2024.

38 Mahdyamam, “Saudi Unveils Two Major Biodiversity Development Projects” (June 23, 2021) https://english.madhyamam.com/middle-east/saudi-arabia/saudi-arabia-unveils-two-major-biodiversity-developments-projects-814159 accessed January 12, 2024; see also Abdulaziz S. Alatawi, “Conservation Action in Saudi Arabia: Challenges and Opportunities” (2022) 29 Saudi Journal of Biological Sciences 5, 3466.

39 See Chapter 2. See also Damilola Olawuyi, Environmental Law in Arab States (Oxford University Press 2022) 245274; also, Reginald Victor, Sustainable Mountain Development in the Middle East and North Africa: From Rio 1992 to Rio 2012 and beyond (FAO, 2012) www.fao.org/3/cc7226en/cc7226en.pdf accessed January 12, 2024.

40 Victor (n 39). See also Fakhoury and AlHaddadin (n 11) 4–5.

41 Olawuyi (n 30).

42 J. Beard, “Eight Asset Managers Unite for One Planet Initiative” (City Wire, July 11, 2019) https://citywireselector.com/news/eight-asset-managers-unite-for-one-planet-initiative/a1249346 accessed January 25, 2024.

43 R. Sharma, “Sovereign Wealth Funds Investment in Sustainable Development Sectors” (UN 2017) www.un.org/esa/ffd/high-level-conference-on-ffd-and-2030-agenda/wpcontent/uploads/sites/4/2017/11/Background-Paper_Sovereign-Wealth-Funds.pdf accessed January 12, 2024.

44 Mahdyamam (n 38).

45 See Hilary C. Bell, “Tackling the Legally Disruptive Problem of Climate Change with Disruptive Legal Education” in Damilola S. Olawuyi (ed), Climate Change Law and Policy in the Middle East and North Africa Region (Routledge 2021).

46 United Nations, “Transforming our World: The 2030 Agenda for Sustainable Development” (October 21, 2015) UN Doc A/RES/70/1 https://sdgs.un.org/2030agenda accessed January 12, 2024. See also Sustainable Development Solutions Network (SDSN), “17.9 Enhance International Support for Implementing Effective and Targeted Capacity Building in Developing Countries to Support National Plans to Implement All Sustainable Development Goals, Including through North–South, South–South, and Triangular Cooperation” https://indicators.report/targets/17-9/ accessed January 25, 2024.

49 See Chapter 2.

50 ASSELLMU, Constitution of the Association of Environmental Law Lecturers in Middle East and North Africa Universities (Adopted in Settat, Morocco in 2019).

51 Salam Al-Zahran, “Conference on: Law on Biodiversity, Nature Conservation, and Cultural Heritage Protection in the Middle East and North African Region” www.kas.de/en/web/rspno/veranstaltungsberichte/detail/-/content/conference-on-law-on-biodiversity-nature-conservation-and-cultural-heritage-protection-in-the-middle accessed January 12, 2024.

52 See Jenni Ramos and Zaneta Sedilekova, “Biodiversity Risk: Legal Implications for Companies and Their Directors” https://commonwealthclimatelaw.org/wp-content/uploads/2022/12/CCLI_Biodiversity_risk_paper_2022.pdf accessed January 12, 2024.

53 Footnote Ibid. See also D. Olawuyi, “Climate Justice and Corporate Responsibility: Taking Human Rights Seriously in Climate Actions and Projects” (2016) 34 Journal of Energy and Natural Resources Law 27.

54 Ramos and Sedilekova (n 50). See also World Economic Forum, “Nature Risk Rising: Why the Crisis Engulfing Nature Matters for Business and the Economy” (January 2020).

55 See TNFD (n 18).

56 Damilola Olawuyi, The Human Rights-Based Approach to Carbon Finance (Cambridge University Press 2018) 125.

57 See Chapter 1. See for example, Friends of Nature, Shan Shui Conservation Centre, and Wild China Film v China Hydropower Engineering Consulting Group in China (2020), in which the Chinese Kunming Intermediate People’s Court ordered the suspension of work on the construction of hydropower on the Jiasa River to protect this last major habitat of the endangered green peafowl, which is the only native peafowl in China. Li Yunqi, “Green Peafowl’s Last Habitat vs. 3.7-Billion-Yuan Dam” https://news.cgtn.com/news/2020-03-21/Green-peafowl-s-last-habitat-vs-3-7-billion-yuan-dam-P2bT7sSi5i/index.html accessed January12, 2024.

58 See Guillaume Futhazar et al., Biodiversity Litigation (Oxford University Press 2020) 810.

59 A good example is the Energy and Biodiversity Initiative which was established to “to develop and promote practices for integrating biodiversity conservation into upstream oil and gas development.” IUCN, The Energy and Biodiversity Initiative https://portals.iucn.org/library/efiles/documents/2003-037.pdf accessed January 12, 2024.

60 See Chapter 16.

61 See United Nations Working Group on Business and Human Rights (UN WGBHR), “Corporate Human Rights Due Diligence: Emerging Practices, Challenges and Ways Forward” report to the UN General Assembly, October 2018 (A/73/163). See also UN General Assembly, Resolution A/RES/76/300, “The Human Right to a Clean, Healthy, and Sustainable Environment” (July 28, 2022).

62 UN WGBHR (n61).

63 Taskforce on Nature-related Financial Disclosures (n 18) 33–35.

64 Jenni Ramos and Zaneta Sedilekova (n 50). See also Stefano Giglio, Theresa Kuchler, Johannes Stroebel, and Xuran Zeng, “Biodiversity Risk” (April 2023) www.nber.org/papers/w31137 accessed January 12, 2024.

65 Giglio et al, Footnote ibid.

66 Footnote Ibid. See TNFD (n 2) 75–80.

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  • Lessons Learned and Future Directions
  • Edited by Damilola S. Olawuyi, Hamad Bin Khalifa University, Doha, Qatar, Riyad Fakhri, Hassan 1st University, Settat, Morocco
  • Book: Biodiversity and Nature Conservation Law and Policy in the Middle East and North Africa Region
  • Online publication: 06 February 2025
  • Chapter DOI: https://doi.org/10.1017/9781009519663.018
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  • Lessons Learned and Future Directions
  • Edited by Damilola S. Olawuyi, Hamad Bin Khalifa University, Doha, Qatar, Riyad Fakhri, Hassan 1st University, Settat, Morocco
  • Book: Biodiversity and Nature Conservation Law and Policy in the Middle East and North Africa Region
  • Online publication: 06 February 2025
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  • Lessons Learned and Future Directions
  • Edited by Damilola S. Olawuyi, Hamad Bin Khalifa University, Doha, Qatar, Riyad Fakhri, Hassan 1st University, Settat, Morocco
  • Book: Biodiversity and Nature Conservation Law and Policy in the Middle East and North Africa Region
  • Online publication: 06 February 2025
  • Chapter DOI: https://doi.org/10.1017/9781009519663.018
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