Abstract
Despite international efforts to stop dryland degradation and expansion, current dryland pathways are predicted to result in large-scale migration, growing poverty and famine, and increasing climate change, land degradation, conflicts and water scarcity. Earth system science has played a key role in analysing dryland problems, and has been even incorporated in global assessments such as the ones made by the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services. However, policies addressing dryland degradation, like the ‘Mexican programme for the promotion of sustainable land management’, do not embrace an Earth system perspective, so they do not consider the complexity and non-linearity that underlie dryland problems. By exploring how this Mexican programme could integrate the Earth system perspective, this paper discusses how ’Earth system’ policies could better address dryland degradation and expansion in the Anthropocene.
Introduction
Our planet has been suffering major changes, with increasing dryland degradation and expansion as one of the many symptoms. Drylands cover around 46.2% of the world’s land surface, 1 which (regardless of current international efforts to stop dryland expansion) illustrates a worrisome increase with respect to the last estimation of 41% published in 2005. 2 If this trend does not change, other global problems will arise, such as large-scale migration, growing poverty and famine, and increasing climate change, land degradation, conflicts, and water scarcity 3 . Although in the policy arena responding to these problems has not been easy, recent efforts such as the Earth System Governance project, have been exploring the integration of the Earth system perspective in political solutions and governance mechanisms for better addressing global change. 4 This piece aims to contribute to those existing endeavours, by exploring how the Earth system perspective can be integrated into the Mexican policies for combating desertification, and afterwards, how ’Earth system’ policies could better address dryland problems in the Anthropocene.
Earth System Science to Support Dryland Policies
Earth system science has supplied a new understanding of our planet, better known as the Earth system approach. 5 This approach looks at the world as a single and complex system composed of the anthroposphere, geosphere and biosphere. 6 Accordingly, this approach is key in the institutional efforts for understanding and addressing global challenges, such as dryland problems, 7 as it maps all the processes and feedback relationships among Earth system components, including the human element. 8
Although policymakers are increasingly using Earth system science terminologies, such as ‘Anthropocene’ 9 or ’planetary boundaries’ 10 to described how human action is the primary cause of global change, there are further integral challenges to be tackled when limiting and regulating human activities. 11
There are no simple solutions to solve complex global problems. However, global dryland expansion can be used as an argument that mainstream laws and policies have not been effective in stopping dryland degradation and expansion. So, it is time to design more comprehensive policies with the embedded Earth system perspective, more suitable with the current understanding of dryland problems. Of course, exploring these implications will require a more practical analysis.
Mexico Against Desertification
64.5% of Mexican territory is covered by dryland 12 and 92.4% 13 of these drylands are undergoing desertification. Between 1993 to 2002, 1.7 million ha of Mexican dryland was lost because of changes in their use and vegetation coverage. 14 These changes (mainly due to agriculture) have led to increased soil erosion and water overexploitation. 15 Ultimately, this has resulted in increasing desertification and dryland exposure to climate change impact. 16
After ratifying the 1994 UN Convention to Combat Desertification, 17 Mexico acquired international commitments to establish an action programme against desertification. In 2006, Mexico created a “Programme to Combat Desertification and Drought”. 18 Moreover, in 2008 it also created the Decennial Strategic Plan 2008–2018 and the National Action Plan, both to Combat Desertification. 19 Overall, the objectives of these plans and programmes were the conservation and protection of vegetation, strengthening forestry and agriculture, promoting environmental education, and restoring degraded ecosystems. 20 Specific actions included training workshops for improving agricultural sustainability, strengthening dryland monitoring, restoration of dryland vegetation, and the creation of a governmental department for combating desertification. 21 However, between 2002 to 2011, 2.3 million ha dryland was lost because of changes in their use and vegetation coverage, despite the above actions. 22
Accordingly, in the two periods above (1993–2002 and 2002–2011), dryland loss (later leading to desertification) increased by about 26%. 23 Therefore, a potential conclusion is that anti-desertification policies were not effective. Furthermore, other programmes designed with the same actions and objectives were created, 24 although, there is not up to date data on dryland loss to analyse their effectiveness. Finally, the latest effort to address desertification is the ‘Mexican programme for the promotion of sustainable land management’, launched in 2016. 25 This is a coordinated effort between the Food and Agriculture Organization (FAO) and the Mexican government. However, it was only implemented in three micro regions, and given its high costs it is not clear if it can be expanded across the nation.
Why did these Programmes Fail?
Around 75% of dryland loss is due to agricultural activities
26
which is why some of the actions for addressing desertification were directed to achieve agricultural sustainability. Yet, the programmes described above did not consider some key aspects, shown as highly relevant by Earth system literature. For example: The interaction of slow (e.g. soil erosion) and irregular (e.g. precipitation) variables that lead to desertification.
27
The dryland social and ecological challenging conditions that undermine human capacity to adapt to environmental uncertainty (e.g. poverty and water shortage).
28
Climate variability and market dynamics shaping local agriculture. For instance, crop yields are affected by heatwaves, while trade agreements lead to an increase in agricultural activities.
29
Recognising dryland’s prima facie right to access the needed ecosystem services to maintain ecological functions and structures. For instance, freshwater availability to support natural vegetation and prevent soil erosion.
30
‘Earth System’ Policies for Addressing Dryland Degradation and Expansion in the Anthropocene
The above highlight social and ecological complexities that were overlooked by the Mexican programmes addressing desertification. In order to integrate the Earth system perspective and better tackle these complexities, policies should consider three aspects: adaptiveness, system regulation and justice provision". Firstly, the processes of social change for responding to environmental uncertainty; henceforth referred to as ‘adaptiveness’. This will allow, natural resource-based livelihoods found in water-scarce areas, to better adapt to climate change. Avoiding natural resource overexploitation and fostering collaboration and local management is critical for achieving adaptiveness. Secondly, policies should be able to limit economic activities at least to a point where they do not surpass local social and ecological dynamics; henceforth referred to as ‘system regulation’. For instance, between 2012 to 2015, four municipalities located in northern Mexican drylands increased their agricultural frontier by 338%, in order to meet market demands. 31 This resulted in increasing water overexploitation, grassland loss, soil erosion, and conflicts over water access, significantly threatening agriculture’s continuity in the area. Policies need to foresee the social and ecological effects at the local level, resulting from agricultural production and international trade agreements. Thirdly, policies need to incorporate nature in the scope of justice, that is, policies need to be reasonable with the ecological conditions required for maintaining the structures and processes that sustain all life forms; henceforth referred to as ‘justice provision’. Conserving the ecosystems which have not been damaged by humans, is paramount for ensuring our collective future. 32 Therefore, policies need to aim for a more equitable distribution of ecosystem services between humans and nature, so drylands can maintain the structures and conditions needed for their ecological processes. Justice needs to be provided accordingly.
Recommendations for Policymaking in the Anthropocene
Addressing dryland problems requires better integration of policymaking and Earth system science. It is important because Earth system science has shown how human activities are the main drivers of global change, like dryland degradation and expansion. Global assessments such as the IPBES Assessment Report on Land Degradation and Restoration 33 have included Earth system research. There, it can be seen that dryland problems are shaped by complex social conditions (e.g. marginalisation) and environmental uncertainty (e.g. climate change).
Accordingly, when aiming to address complex global problems, such as dryland degradation and expansion, policies should incorporate adaptiveness, system regulation, and justice provision. Of course, there will hardly be an existing blueprint for implementation. However, we could at least start with policies (e.g. plans and programmes addressing desertification) which should be able to respond to the following four questions and provide the necessary solutions. Firstly, is the policy fostering collaboration and stakeholder participation in local decision-making and management processes? Secondly, is the policy enabling economic activities without compromising the sustainability of local livelihoods? Thirdly, is the policy considering slow variables (e.g. loss of soil fertility) and environmental uncertainties (e.g. droughts or floods)? Fourthly, is the policy foreseeing the required measures for ensuring an equitable distribution of natural resources between humans and nature?
If all the responses to those questions are yes, then it can be considered that the policies are more suitable to address global problems, such as dryland degradation and expansion in the Anthropocene epoch.
Footnotes
Alisher Mirzabaev and others, ‘ Desertification’ in J Skea, E Calvo Buendia, V Masson-Delmotte, HO Pörtner, Shukla, P Zhai, R Slade, S Connors, R van Diemen, M Ferrat, E Haughey, S Luz, S Neogi, M Pathak, J Petzold, D.C. Roberts and P Vyas, E Huntley, K Kissick, M Belkacemi, J Malley, J. Portugal Pereira (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 (In press 2019).
Uriel Safriel and others, ‘Chapter 22 Dryland Systems. Ecosystems and Human Well-Being: Current State and Trends. Volume 1, Findings of the Responses Working Group of the Millennium Ecosystem Assessment.’ (N Hassan R., Scholes, R., Ash ed, Island Press 2005).
Sarah Burch and others, ‘New Directions in Earth System Governance Research’ (2019) 1 Earth System Governance 100006; Louis J Kotzé and Rakhyun E Kim, ‘Earth System Law: The Juridical Dimensions of Earth System Governance’ (2019) 1 Earth System Governance 100003.
Eckart Ehlers and Thomas Krafft (eds), Earth System Science in the Anthropocene (Springer 2006).
Will Steffen and others, ‘The Emergence and Evolution of Earth System Science’ (2020) 1 Nature Reviews Earth & Environment 54.
Drylands are ecologically limited by water scarcity, while on the social, people living in drylands are considered the poorest and most marginalised people in the world. Accordingly, here ‘dryland problems’ refers to these coupled social-ecological limitations and challenges underlying dryland degradation and expansion.
The Anthropocene refers to a new geological epoch where humans are the main drivers of global change, and some of the Earth system processes are no longer taking place in the stable Holocene-like state conditions; for more information see Paul J Crutzen and Eugene F Stoermer, ‘The “Anthropocene”’ (2000) 41 IGBP Newsletter 17; Steffen and others (n 7).
The planetary boundaries framework estimates the safe operating space for humanity (the only state we know that can support our civilisation) with respect to the Earth system functioning; for more information see Will Steffen and others, ‘Planetary Boundaries: Guiding Human Development on a Changing Planet’ (2015) 347 Science; Johan Rockström and others, ‘Planetary Boundaries: Exploring the Safe Operating Space for Humanity’ (2009) 14 Ecology and society.
Thomas Sterner and others, ‘Policy Design for the Anthropocene’ (2019) 2 Nature Sustainability 14.
CONAFOR and UACH, ‘Línea Base Nacional de Degradación de Tierras Y Desertificación. Informe Final Y Anexos I Y II’ (2013).
Gabriel Lopez Porras, Lindsay C Stringer and Claire H Quinn, ‘Corruption and Conflicts as Barriers to Adaptive Governance: Water Governance in Dryland Systems in the Rio Del Carmen Watershed’ (2019) 660 Science of The Total Environment 519; Paulina Alejandra Pontifes and others, ‘Land Use/land Cover Change and Extreme Climatic Events in the Arid and Semi-Arid Ecoregions of Mexico’ (2018) 31 Atmosfera 355.
ibid.
United Nations Convention to Combat Desertification in those Countries Experiencing Serious Drought and/or Desertification, Particularly in Africa (adopted 14 October 1994, entered into force 26 December 1996, in accordance with article 36(1)) 33480 UNTS 1954; this document was ratified by Mexico in 3rd April 1995.
SEMARNAT and CONAFOR (n15).
CONAFOR and UACH (n13).
SEMARNAT and CONAFOR (n15).
This was called ‘National System to Combat Desertification and Degradation of Natural Resources’.
Pontifes and others (n16).
SEMARNAT and CONAFOR (n15); CONAFOR and UACH (n13).
For instance, the “National Sustainable Land Management Programme to Combat Land Degradation and Desertification in Mexico” launched in 2013.
SEMARNAT (n14).
Gabriel Lopez Porras, Lindsay C Stringer and Claire H Quinn, ‘Seeking Common Ground in Dryland Systems: Steps Towards Adaptive Water Governance’ (2020) 12 Water 2020, Vol. 12, Page 498–498.
Geoffrey Garver, ‘A Systems-Based Tool for Transitioning to Law for a Mutually Enhancing Human-Earth Relationship’ (2019) 157 Ecological Economics 165.
See Lopez Porras, Stringer and Quinn, ‘Seeking Common Ground in Dryland Systems: Steps Towards Adaptive Water Governance’ (n30).
IPBES (n4).
