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Making Peace with Nature? Reflections on the 2024 United Nations Biodiversity Conference in Cali, Colombia

COP16 sign by the official conference venue in the northern outskirts of Cali (Source: Author)

By Fariborz Zelli

Three weeks ago, the 16th conference of the parties (COP) to the United Nations Convention on Biological Diversity (CBD) ended in the Colombian city of Cali. In the 32-year history of these biannual meetings, the negotiations during the Cali COP were remarkable in various regards, for both achievements and disappointments – and for similarities to the UN climate COP that took place in Baku only two weeks later.

1. The Official Negotiations: Making somewhat peace with Nature

What worked well…

Arguably the biggest success – and where the COP delivered mostly on its motto “Making Peace with Nature” – was the progress made on Article 8 (j) of the biodiversity convention. The article highlights the importance of traditional knowledge and practices, and hence directly relates to the role that indigenous and other local communities play for safeguarding biodiversity around the planet. With the headway made on these questions, the Cali COP has also vital implications for our Lund-based team’s research on the role of environmental human rights defenders (EHRD).

The discussions around Article 8 (j) had been key for the Colombian hosts around conference President and Colombian environmental minister Susana Muhamad as well as for the Colombian government under President Gustavo Petro. Thanks to the diplomacy of the COP leadership, delegates agreed in the final hours to establish a new subsidiary body to protect indigenous communities and local populations as defenders of nature. They further decided to acknowledge the role of people of African descent in the implementation of the biodiversity convention, going back to another initiative tabled by the conference hosts. 

With their decision the delegates created the precedent of placing a political organ dedicated to indigenous communities and human rights under the auspices of a global environmental institution – and they thereby recognize the strong overlaps between biodiversity and human rights. While the new subsidiary body now must be filled with life, its sheer establishment guarantees that concerns of indigenous and local communities will be more strongly integrated in discussions and decisions at future biodiversity COPs. Beyond the immediate context of the CBD, the body provides a new frame of reference with an institutional underpinning for EHRDs across the globe. Ideally, it can help facilitate a much-needed denser network of international and domestic law to protect indigenous and local communities in biodiversity hotspots.

This conference outcome is even more notable as Colombia is the country with the highest number of assassinations of EHRDs worldwide. This sad figure is, absurdly, connected to the country’s peace process, which had started in 2016 when an accord between the Colombian government and the FARC rebels ended an over fifty years long civil war. With the FARC giving up control over a large part of Colombian territory, the lands of indigenous, peasant, Afro-descendant and other local communities also became accessible to new threats, from legal and illegal mining to the expanded areas of operation of Colombian, Mexican and other international drug cartels. The new CBD subsidiary body will not be able to solve these problems fundamentally, but it may alleviate some of them – by more widely acknowledging the efforts that EHRDs in Colombia and elsewhere are making to protect nature in conjunction with their own cultures and livelihoods.

Banners in the Green Zone on indigenous communities as biodiversity defenders (Source: Author)

The Cali COP also saw progress on further important topics. This includes another agenda item of high relevance for indigenous and local communities, and for North-South relations in general. Delegates agreed on a new multilateral mechanism to fairly share the benefits from the use of genetic resources, and to do so based on genetic sequences of biodiversity stored in databases. Companies who use such digital sequence information (DSI) are now expected to pay a portion of their profits and revenues to the new ‘Cali Fund’. This would apply, for instance, when plant genetic resources with an origin in Sub-Saharan Africa or the Amazon are used by pharmaceutical companies in the Global North. Notably, 50% of the fund shall be allocated to indigenious peoples and local communities. Since the new mechanism is voluntary, however, companies are under no legal obligaton to compensate countries of origin or respective actors therein.

What didn’t work well…

Notwithstanding these and other positive results – e.g. on mainstreaming biodiversity into infrastructure, and, after eight years of negotiations, on a new process to identify ecologically significant marine areas – the Cali COP leaves behind a lot of unfinished business. No significant progress was made on two of biodiversity negotiations’ major bones of contention: 1) on implementing the new core of the CBD treaty family, the 27 goals of the 2022 Global Biodiversity Framework (GBF), which had been adopted at the last COP in Montreal; and 2) on the financial mechanism and resources to support respective implementation efforts. Negotiators could not reach substantial agreement on neither of these two essential matters. In fact, with an increasing number of delegates leaving for their flights home, the COP plenary was no longer permitted to take any decisions in the final conference hours. Instead, the conference was suspended unceremoniously, with a resumed meeting expected to take place in the coming months. 

When it comes to the first controversial aspect of implementation mechanisms, delegates at Cali could not fill important gaps in the so-called “stocktake” – a global review process, which, by 2026, shall hold countries accountable for implementing the GBF. To be fair, this implementation and review gap of biodiversity negotiations is the consequence of a more fundamental problem that marks global environmental diplomacy today: a hollowing-out of what is actually multilateral in the respective treaties and agreements, with things not adding up.

Environmental diplomacy has never been easy, seeking to address systemic and complex problems while often being down-prioritised in comparison to international security or trade. Over the past ten years or more, however, we have been witnessing a particular trend in global environmental politics: Major negotiations provide ambitious but voluntary goals while not specifying what the specific contributions of each country, or at least some countries, to these goals should be (as was still the case e.g. in the 1997 Kyoto Protocol on climate change). Instead, each country may come up with their own individual implementation plans and objectives, which only undergo voluntary review processes and which, when added together, are far from reaching the overarching goals. 

The GBF with its ambitious, yet non-binding set of 27 targets is just the last prominent example for this logic of window-dressing of multilateral environmental deals. Others include the Sustainable Development Goals (SDGs), and the Paris Agreement on climate change with its 1.5°C goal, both adopted in 2015 and, like the GBF, built around ambitious and internationally renowned goals while leaving essential questions of individual country contributions and implementation out of the multilateral package. The voluntary country reports may bear different names and acronyms in these three contexts – VNRs (Voluntary National Reviews) for the SDGs, NDCs (nationally Determined Contributions) for the Paris Agreement, and NBSAPs (National Biodiversity Strategies and Action Plans) for the GBF. But with the first rounds of these reports coming in, they share similar degrees of disappointment: Based on the VNRs the 2024 SDG Report revealed that only 17% of the SDG targets were on track for 2030; summing up all NDCs we can no longer exclude the possibility of surpassing 2.9°C of global warming by 2100; and before CBD-COP16 more than 80% of the 196 parties to the GBF had missed the deadline to submit their revised NBSAPs

With this fixation on voluntary goals as the in-built problem of international environmental diplomacy today, it should not come as a surprise that the implementation gap is haunting COPs like the one in Cali. Negotiators and observers show a lot of good will and insight and discuss all sorts of mechanisms for implementation and review until the last minute, but these hardly find their way into decisions. 

The same window-dressing deja vu applies to financing, the second major contentious issue in Cali. Once again not unsimilar to climate negotiations (with e.g. the Green Climate Fund or the new Loss and Damage Fund), it is comparably easy for countries to agree on joint financial targets rather than on specific activities to keep these promises, e.g. on a mechanism like the Cali Fund on benefit sharing. Similar to major sets of targets like the GBF in 2022, a new fund makes for a presentable final conference result to the media. Yet, agreeing on a fund as such keeps more important and more sensitive modalities unaddressed, e.g. how much certain countries actually should and will contribute, or how voting rights on the use of the funds are distributed. An illustration of the divergent views on these specific questions is a 98-page-long non-paper published by delegation co-chairs at Cali, packed with wishlists on resource mobilization through 2030 that negotiators could not agree on. 

Taking this into account, the failure to establish a proper global biodiversity financing mechanism at Cali, no matter how superficial, is outright underwhelming. The CBD now must continue working with an interim trust fund, the 2023 Global Biodiversity Framework Fund, for which pledges have been comparatively low in Cali. With currently a bit over US$ 400, the fund falls significantly short of developed countries’ commitments to provide US$ 20 bn annually in international biodiversity financing by 2025. 

The story behind this failure is not only one of lack of willingness of developed countries to accept larger responsibility for global biodiversity loss. It is also a story of power and political control. In the absence of a proper CBD fund, the interim financing mechanism is operated by the Global Environment Facility (GEF), a multilateral financial institution whose funds are administered by the World Bank and that has provided grants for environmental protection activities in developing countries since 1991. 

Funding decisions are taken by the GEF Council which consists of 14 members from developed countries, 16 from developing countries, and two from economies in transition – a constellation that allows donors to keep considerable control over where their money is going. By contrast, a global financing instrument for biodiversity under the authority of the COP, as conference President Susana Muhamad suggested on the last day in Cali, would have given developing countries a voting majority over these financial flows. By rejecting such an instrument, developed countries prioritised their control as donors over substantial progress on global biodiversity protection.

This outcome is even more underwhelming when taking into consideration that Cali negotiations were not severely affected by US elections. Unlike for the current climate COP in Baku where the US delegation is a lame duck, the Cali COP ended three days before Trump’s victory. Due to the missed opportunities at Cali, however, US elections will effectively have a big effect on this COP after all. Even though the US is not a party to the CBD, the incoming administration will cast a shadow on further negotiations, including at the resumed COP in a few months. For the next four years in general, we can expect a considerable drop in US support for UN environmental conferences and their goals, which will also impact the strategies of other parties. 

Connected to these disappointments on implementation and financing, the COP has suffered from typical rituals that have become familiar traits of multilateral environmental negotiations over the years. One of these is the who-blinks-first mentality of major negotiationg blocks. Negotiators often wait with major concessions on key issues until the last moments of a COP. This approach entails, first, all sorts of procrastinations during most of the two weeks of the conference, e.g. overproportionally long discussions about technical details, and second, a crescendo towards a melt-down and last-minute spree of decisions. As Cali has shown, this final act may even come too late when most seats in the theatre are already empty.  

Another ritual that can hit the brake on negotiations – and certainly did so in Cali – was the typical high-level segment in the second week of environmental COPs. When heads of states and environmental ministers join negotiations for a few days to address the COP plenary this may well serve to raise the global publicity of negotiations, and of these very heads of states and ministers themselves. However, this intermission of governmental leaders, a type of ‘COP inside the COP’, also tends to interrupt the actual negotiation efforts in the important final phase of the conference.

Related to this, backroom diplomacy at environmental COPs has considerably increased over the last years. To reinvigorate discussions on controversial issues, conference hosts happily act as honest brokers and summon a handpicked selection of country delegates or leaders behind closed doors. However, using such backroom diplomacy as an excessive element can also backfire, as it loses some of its magic and keeps the actual negotiations in waiting. In Cali, those closed doors did not even open in time before too many delegates had left town. 

2. Non-Governmental Engagement: Some People’s COP

What worked well…

COP President Susana Muhamad claimed that COP16 in Colombia will be remembered for being “La COP de la gente”, the people’s COP. She has a point with respect to the decisions on indigenous communities and local populations, but also with a view to the wider engagement of civil society and the local public. One of the highlights during the two weeks in Cali was the designated area for civil society activities, the so-called ‘Green Zone’. In recent years, organisers of environmental COPs often carefully choose to spatially separate this area the from official negotiation venue (the ‘Blue Zone’) – for security reasons, but certainly also to avoid disturbances by larger protests. Cali was no different in that regard, with the Blue Zone in a large conference centre on the north end of the city, and the Green Zone being placed in a park right in the heart of Cali. 

Green Zone side-event with indigenous representatives from Putumayo, Colombia (Source: Author)

Nonetheless, a benefit of this spatial distance was that the local population took a much stronger interest in Green Zone activities and, especially during the first COP week, turned the zone into a festival of cultural encounters. Many indigenous associations and communities, mostly from Colombia, had come to Cali to present their traditions in numerous exhibits, but also to talk about their needs and the challenges they face in a series of side-events. In these they repeatedly stressed their delicate role as defenders and guards of biodiversity. They reminded listeners that in recent years the loss of primary forest in the Amazon has been significantly lower in indigenous than in non-indigenous territories. In defending their own livelihoods, these communities have become, intendedly or not, frontline implementers of the very Global Biodiversity Framework that negotiators were debating some kilometers further north. 

For many Colombians the Green Zone in Cali may have been the first major opportunity for direct exchanges on the indigenous heritage of their country, and about the various threats the respective communities are facing. These encounters and learning processes, one hopes, may contribute to a wider recognition and understanding of the role of environmental human rights defenders – and to preserving traditional ecological knowledge, lifestyles and cosmologies of these communities and their invaluable insights for preserving biodiversity. That alone would make this COP a success story, no matter what happened in the actual conference centre in the outskirts of the city.

What didn’t work well…

With 23,000 registered participants, 46% more than at the previous COP, Cali hosted the biggest biodiversity COP to date. While this number is dwarfed by attendance figures of UN climate conferences (85,000 in Dubai last year; 65,000 at the current COP in Baku), the steep increase from 2022 implied several challenges.

For one, the organization of side-events in the Blue and Green zones was far from optimal, if not outright overburdened. Blue Zone organisers accepted about a quarter of the ca.1,200 proposed events, but only published the selection and actual schedule about a month before the start of the conference. Green Zone organisers took the decision to shorten the original submission period for side-event proposals in the midst of application process. These organizational mishaps posed severe challenges to the activities and travel plans of many civil society actors, especially for those from developing countries. 

Blue Zone side-event on the nexus of peace and biodiversity (Source: Author)

While figures went up for all types of attendants between the 2022 and 2024 COPs, they did so unproportionally for business and industry delegates. Most of these represented sectors like pharmaceuticals, fossil fuels, agrochemicals and pesticides, food and beverage processing and biotechnology. A total of 1,261 such delegates registered for the Cali COP, more than doubling business representation compared to the previous UN biodiversity summit in Montreal.

To get somewhere near reaching the GBF targets, it no doubt is essential to involve businesses across implementation activities. Without attracting investors and innovators, most of these activities will remain impossible. This notwithstanding, the soaring figures of business delegates raise some concerns. First, if this trend continues it will manifest a systemic imbalance among non-governmental actors in future COP representation, to the disadvantage of e.g. vulnerable communities or scientific institutions.

Second, certain lobbyists may seek to push back progress on key questions, as, for instance, many biotech representatives attempted around negotiations on the new benefit-sharing mechanism at COP16. And third, the large global attention that UN environmental summits are receiving also makes them welcome platforms for greenwashing. To put this carefully: it may have been advisable for organisers in Cali to gauge the possible consequences of business-showcasing in their events more cautiously beforehand. 

One example was the advertisement for Smurfit in Cali’s Humboldt House, which organized a total of 180 external events on culture and biodiversity during the COP. Smurfit-Kappa, Europe’s leading corrugated packaging company, has repeatedly been the target of severe accusations by indigenous and campesino communities in Colombia’s Cauca region. The communities are impacted by Smurfit-Kappa’s intensive monocrop pine and eucalyptus plantations and have been trying to reclaim their land from the company.   Another multinational met more resistance at Cali. The self-presentation the Canadian company Libero Cobre as a biodiversity champion provoked a protest rally by indigenous communities. The company had acquired four mining titles in southern Colombia in 2018 and since met protests by members of local Nasa and Inga communities for fear of groundwater contamination, forest loss, splitting the community and disregarding rights of prior informed consent. On another note, the Swedish embassy’s decision to host its official reception for Sweden-based COP participants in Cali’s local IKEA store may have raised quite a few eyebrows. 

3. The Way Forward – A Tale of two COPs

Many of the challenges mentioned, from implementation and financing gaps to ritualistic aspects, lobbying and greenwashing, have been haunting both UN biodiversity and climate negotiations for years. It thus does not come as a surprise that many of the reform suggestions that are made for UN climate summits are also applicable to biodiversity COPs. At the occasion of the ongoing UN climate COP in Baku, eminent politicians and researchers published an open letter with the Club of Rome in which they urged several reforms – and most of their suggestions sound as if they had been written for the biodiversity COP Cali. 

To address the ritualistic and last-minute showdown nature of COPs the authors recommend a “shift away from negotiations to the delivery of concrete action”. To achieve this, COPs could be transformed to smaller, but more frequent and solution-oriented meetings. Such a reform would give delegates more space and time to focus continuously on sensitive but essential modalities of financing and implementation, i.e. to actually fill the envelopes and go beyond superficial establishments on targets and funds. As for implementation, future meetings could ideally be supplemented by enhanced reporting and benchmarking mechanisms to monitor country progress continuously and hold countries accountable for reaching the GBF targets. More targeted COP meetings could direct more negotiating efforts towards criteria for disbursing funds and tracking mechanisms for financial flows, and thereby help overcome the current stalemate over a future biodiversity funding mechanism.

Another side-effect of smaller, more frequent and targeted COPs could be the equitable representation of non-governmental actors. Cutting back to a smaller presence of observers at the official Blue Zone altogether could go hand in hand with balancing figures among business, NGO and scientific representatives – without necessarily having to compromise on the scope of civil society activities in the Green Zone.

Various observers have also called for holding joint climate and biodiversity COPs in the future. Such an approach would have its benefits considering an increasing number of cross-cutting topics, from the impacts of climate change on biodiversity to the use of forests as carbon stocks or the protection of indigenous communities as environmental change agents. 

There are some caveats though, and not only given the current sizes of both types of conferences. As the last two world environmental summits – 2002 in Johannesburg and 2012 in Rio – have shown, negotiating too many sensitive aspects in one package may reduce the opportunity of any notable deal at all. Moreover, there is a risk that biodiversity questions are subordinated to certain concerns or logics in climate negotiations. For instance, the latter feature a larger set of market-based approaches like offsetting and tradable certificates. While quantifying carbon limitation efforts is a challenge, doing so for valuing biodiversity may be often impossible, or simply not desirable. One case in point that demonstrates this is the so-called REDD+ mechanism (Reducing Emissions from Deforestation and Forest Degradation) under the UN climate regime. As of 2022 REDD+ activities covered more than 60% of the forest area in developing countries. While the mechanism values and quantifies the carbon storage aspect of forests (by covering opportunity costs of avoided deforestation), it side-lines other important forest functions. The merits of this mechanism notwithstanding, it exemplifies how core aspects of biodiversity are today negotiated from a climate perspective. 

Finally, the selection processes of future COP venues need to be overhauled. Delegates in Cali decided that the next CBD COP in 2026 will be held in Armenia. Notably, the main contender was Azerbaijan, the very host of the currently ongoing UN climate conference. To say the least, a UN biodiversity summit should not turn into a sideshow of geopolitical tensions between two neighbouring countries. What is more, as not only the current climate COP shows, the choice of venue can have a severe impact on the course of negotiations, and not always for the better. Praising fossil fuels as a “gift from God”, as Azerbaijani head of state Ilham Aliyev did in his inaugural address to the climate COP in Baku, has set an unfortunate tone for that meeting. 

The next biodiversity COP is now spared a similar fate and will not take place in a country where 90% of the export economy relies on oil and gas. Still, we need stricter eligibility criteria for future COP Presidencies. The Cali COP with its achievements on indigenous people and local communities demonstrated what a difference it can make to hold a COP in a mega-biodiverse country with an engaged host government. Let us hope for similarly sensible placements in the future. Addressing the sixth mass extinction is a too serious issue to be left to geopolitics and country greenwashing. 

November 21, 2024

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Environmental Change in Conflict and Post-conflict Northern Uganda: A Geographical Analysis to Understand Prospects for Sustainable Peace and Development in the Region

Crops and natural vegetation in Northern Uganda. Source: Getty Images. Marck Newman.

We have previously discussed at the Nature of Peace about the usefulness of using remote sense analysis to monitor environmental change in conflict-affected areas. Following up on this, we share in this post some of the findings from our study on vegetation and environmental change in Northern Uganda, published in the The Journal of Environment and Development (open access here). For an in-depth presentation of the research (design and findings) please check our article.

In peacebuilding efforts, it is important to recognize how armed conflicts impact the environment, not only through ecosystem damage and biodiversity loss but also through opportunities for ecological recovery. Both of these outcomes can shape post-conflict paths toward peace and development. In Northern Uganda, the conflict from 1986 to 2008 had a significant effect on both the communities and their surrounding environment. While some regions experienced environmental degradation, others saw ecological recovery. Understanding these dynamics is key for managing natural resources in post-conflict areas and supporting peacebuilding efforts. We explore how vegetation in Northern Uganda changed during and after the conflict, analysing what may have driven these changes and their implications for lasting peace and sustainable development. By examining satellite imagery and existing research, we see a post-conflict ‘greening’ alongside a more balanced pattern of both vegetation loss and recovery at the regional scale. If these changes are linked to agricultural expansion, how agriculture is managed in relation to natural ecosystems will be crucial for peace and development.

Image credit: Getty Images. Mark Newman.

Introduction

There is increasing global recognition that armed conflicts have direct impact on the natural environment (ecosystems, natural resources, biodiversity), as evidenced by the growing number of research (1), policies and reports (2) as well as institutions or organisations who have incorporated peace concerns in their environmental agendas or environmental or ecological concerns in their peace agendas.

While empirical evidence from diverse regions of the world shows that armed conflicts trigger processes of environmental degradation on the ground, less is known about how armed conflicts might also contribute to processes of ecological restoration. This is the case, for instance, of areas previously dedicated to farming, abandoned due to displacement. Both processes – degradation and restoration – have profound consequences for sustainable peace and development in the aftermath of conflict.

The armed conflict between the Lord Resistance Army (LRA) and the National Resistance Movement (NRM)/Uganda People’s Defence Force (UPDF) between 1986 and 2008 in Northern Uganda had profound impacts on local communities and their natural environment (3). The impacts were however not geographically evenly distributed. While some geographical areas have gone through environmental deterioration – due to natural resources overexploitation or infrastructure development – other areas have experienced ecological restoration (4). This historical trend is central to understanding post-conflict natural resource exploitation and management.

In 2013, the Advisory Consortium on Conflict Sensitivity (ACCS) conducted a comprehensive study on post-conflict drivers of conflict in Northern Uganda and concluded that one of the ‘four most serious threats to long term peace’ across the region related to the natural environment (such as competition over natural resource exploitation and access to land; including oil, grazing, forests and over reserves, but also environmental deterioration and natural disasters) and such threats could ‘inevitably return to overt conflict’ (3). In 2015, the Government of Uganda (GoU) stated that tensions over resources (particularly access to land) among people could threaten any peace and development intervention set up to stabilise the region (5). Together with urban growth, high poverty and low education levels, local communities bear a high potential of relapse into violent conflict (6).

Northern Uganda currently faces numerous environmental challenges and conflicts driven by expansion of plantation agriculture, oil exploration and exploitation, and urban growth (7). Nardi (2024) understands that the expansion of the resource frontier towards the Northern region of Uganda during peacetime – lead by large-scale capital – has generated tensions with local communities whose knowledge and understanding of the natural environment are not considered in such economic projects (e.g. oil exploitation, mineral exploration, agribusiness, hydro-energy, etc.). In addition, a growing population demanding energy and food has triggered land use and land cover change which patterns and extent are of environmental concern (6). Scholars have more recently stated that land use and cover change ‘is having a wide range of impacts on the environment and the people of Uganda at different spatial and temporal scales’ (8). One of such impacts can be found in environmental or climate-induced migration (9).

We argue therefore that prospects of sustainable peace and development cannot be properly understood without considerations of the natural environment. The purpose of this article is to understand (a) how vegetation activity has changed in Northern Uganda during and after the armed conflict and (b) possible drivers of environmental change explaining such vegetation activity change. The aim is (c) to comprehend potential implications of environmental change on the sustainability of peace and development.

We analyse environmental changes by examining shifts in vegetation activity at the sub-regional and district levels during the conflict period (2002–2008) and the post-conflict period (2008–2018). Additionally, we observe vegetation activity on a regional scale during the post-conflict years (2008-2018). Our descriptive analysis provides insights into the spatial distribution of vegetation activity trends, using satellite imagery time series to assess the final years of armed conflict and the subsequent recovery period.

Furthermore, we seek to explore the drivers behind these changes in vegetation activity during the post-conflict period, comparing them to trends observed during the conflict in four key sub-regions: West Nile, Acholi, Lango, and Teso. For this, we draw on secondary data from land use and land cover (LULC) studies, predominantly from academic sources. Our explanatory analysis helps us explore the environmental implications of these changes, such as ecosystem degradation and biodiversity loss.

By examining both trends and drivers of vegetation/environmental change, we aim to highlight the crucial role of the natural environment (e.g., as natural resources) in promoting peace and sustainable development. Our findings serve as a foundation for future fieldwork-based research aimed at understanding environmental dynamics in the region, with implications for policymaking and peacebuilding efforts.

The Natural Environment During Conflict and Post-conflict in Northern Uganda

During the second decade of the armed conflict between LRA and UPDF – around 1996 – people from Acholi sub-region were moved to internally displaced people’s camps (IDPC). The relocation of around 1.4 million people led to an uneven spatial distribution of natural resource overexploitation in camps and around them. Between 1985 and 2002 woodlands were lost around towns (Gulu, Kitgum, Lira) and IDP camps due to natural resources overexploitation as a consequence of internal migration and expanding human population which resulted in conversion of natural vegetation to farmland in the southern districts of the region (e.g. Lango).

The paradox is, nevertheless, that the armed conflict worked also as a driver for environmental protection (e.g. vegetation preservation or restoration) in other areas. Vegetation was restored in some of those territories where the LRA rebels were based, or with no easy access by most of the local population. This might explain the higher level of vegetation conservation during that period in particular woody cover west and north of Kitgum where the LRA has been most active (4).

The abandonment of some areas (both by people and livestock) and the concentration of population in others have been clear drivers of vegetation change. However, other factors might be explaining this unequal geography of environmental change, such as biodiversity loss (e.g. due to habitat destruction), population growth, expansion of urban settings and/or farmland, or temporal and spatial variations in the weather (e.g. making some areas more prone to droughts than others). This might be indicating that ecological connections of Northern Uganda with other geographical regions could explain environmental change during conflict time and not only the consequences of the armed conflict itself (e.g. destruction of wildlife habitats that work as corridors).

From 2007, once the violence against civilians deescalated and people started leaving the camps, evidence shows that the Northern region of Uganda became the scene of socio-environmental transformations: urban growth, expansion of charcoal production, logging and high-value timber extraction, oil and mineral exploration and exploitation, agribusiness, land enclosure for nature conservation and the consolidation of new camps for displaced migrants from neighbouring countries.

Various factors, ranging from local to global scales, might explain the environmental changes occurring on the ground in Northern Uganda. According to academic research and policy reports, diverse processes of environmental change – mostly connected to vegetation degradation and biodiversity erosion – are motorised by the increased local population and the insertion of the region into the global economy. We observe, for example: (a) the expansion of farmland for local food production, (b) the increasing charcoal exploitation for energy consumption mainly in Uganda but also bordering countries (8, 10), (c) the increasing oil, mineral and timber exploitation for foreign markets (7), (d) the setup of camps for hosting Sudanese refugees (11), (e) the expansion of large scale agriculture (monoculture plantation) for extra regional markets (11) and (f) the enclosure of forests and savannas for biodiversity conservation and tourism (13). Urban population growth seems relevant to understanding processes of environmental deterioration in particular. Urban population in Uganda increased from less than one million persons in 1980 to about 3 million in 2002 and 7.4 million in 2014 (14). This trend translates also into land cover and use change, usually resulting in environmental degradation and biodiversity erosion. Urban areas have increased with a growth rate of 52% at the national level between 1996 and 2013. In the context of Northern Uganda, it can be observed clear gains in urban land uses, remarkable in Acholi sub-region where there has been 327% increment of urban land area during the period of 1996–2013, but also in neighbouring Lango sub-region during the same period (15). Research has shown that ‘the war economy and the subsequent growth and development of Internally Displaced People’s camps (IDPs) which have been upgraded to urban centres explain the observed patterns of growth in Acholi region’ (15, page 262).

Most of the population of Uganda uses biomass as the main energy source (16; 17). In Northern Uganda, evidence shows that savannas and forests restored during the conflict turned into a rich source of charcoal during post-conflict, particularly to be traded outside the region (18). This particularly the case due to regions previously supplying Kampala were already totally depleted (19).

Research observed that during the post-conflict and peacebuilding period, new actors arrived in the Northern region and scaled up natural resource extraction and trade, for charcoal production and valuable timber logging (6). The fragile land tenure and unstable land access seems to be pushing people to cut down trees or overexploit soils as they are uncertain about the long-term access to natural resources from their land plots (20). This has further accelerated an environmental degradation process, according to different sources.

Unsustainable charcoal production has been reported in Acholi, West Nile, Lango and Teso to name a few of the Northern sub-regions where charcoal is produced and traded in and out of the region. The overexploitation of timber and charcoal production is recognised as one of the major environmental concerns in the North region. For some, ‘charcoal production, and its particular destructiveness, should be understood as a continuation of the violence of the 1986-2006 war between the Lord’s Resistance Army and the Ugandan government’ (6, page 242).

During the period 2010-2015, an estimated number of 250,000 ha of forest per year were lost in the entire country, while between 1990 and 2015, the annual average of lost forest was 122,00 ha. (21). At the same time, forest cover outside protected areas was reduced from 3,331,090 ha in 1990 by 34% in 2005 and by 68% between 2005 and 2015 (21). This might be indicating that areas with high vegetation cover (both forests and grasslands) have been subject of exploitation during peace times (post-conflict period) in the country.

Activities around oil exploration and exploitation along the Albertine Rift have been reported to be detrimental for natural vegetation and polluting (7). Construction activities (e.g. roads, bridges, pipelines, refineries) might explain losses in forest cover in Acholi region (15).

Spatial Distribution of NDVI Trends in Northern Uganda in the Conflict and Post-conflict Periods and suggested explicative drivers

We look into biological activity (photosynthetic activity) that results from both natural and planted vegetation (agriculture). Therefore, increase/decrease vegetation activity does not mean there is an increase/decrease in natural vegetation or biodiversity. Nevertheless, photosynthetic activity is a valid proxy for studying the status and change of vegetation as we will show later.
We studied vegetation trends using remote sense analysis and the Normalised Difference Vegetation Index (NDVI) which have been used to study vegetation dynamics and phenology and trends in vegetation greenness in diverse geographical contexts. For a detail methodological explanation of our study see Nardi & Runnström (2024).

It becomes visually apparent when comparing the NDVI trend maps (Figure 1) that areas with positive trends (in green) are more abundant in the post-conflict period (B) in comparison to the conflict period when larger areas show negative trends (in red) (A).

At this scale of analysis, it is then possible to conclude that Northern Uganda has been turning greener after the cessation of hostilities (B). In the drought stricken Karamoja a ‘greening’ process seems to be taking place since the conflict ended and during the period of analysis (2008-2018), contrary to the conflict period when large extents of areas showed negative trends in vegetation activity (2002-2008).

In general terms, we observe that half of the sub-regions under study (four out of eight): north of Bunyoro, Karamoja, Lango, and West Nile have increased vegetation activity between the conflict and post-conflict periods. West Nile stands out due to the larger difference in mean NDVI trend indicating a positive change in vegetation activity.

On the contrary, the remaining four sub-regions show a reverse trend from positive during the conflict period to negative in the post-conflict period or decreasing positive trends, namely, Acholi, Bukedi, Elgon, and Teso. Two sub-regions stand out in this regard – Bukedi and Elgon – due to the greater difference in the mean NDVI trend in comparison with the rest of the sub-regions.

At district level, it is noticeable that most of the area from all the districts in West Nile and Karamoja sub-region have turned negative or stable NDVI trends in the conflict period into positive ones in the post-conflict period of analysis. Karamoja shows the highest positive trends in all its districts during the post-conflict period where no negative cases are found. On the contrary, all districts in Bukedi and most in Elgon show opposite trends between the periods studied. Elgon sub-region stands out due to the severity of the negative trends in the post-conflict period in comparison to all the districts studied.

During the conflict and post-conflict period of analysis, districts in Lango show dissimilar NDVI trends on average as in the case of districts in Acholi, with some districts presenting negative and others, positive trends. The districts in Teso show that high positive trends during the conflict period have changed to moderate but still positive trends in the post-conflict period.

Finally, a common pattern in all districts studied is that there is less variation of extreme (positive-negative) NDVI trends in the post-conflict period of analysis in comparison to the conflict period of analysis. This is evidenced by the statistical analysis which shows that the standard deviation is smaller in the post-conflict period compared to the conflict period.

Figure 1: Uganda: selected sub-regions. Spatial distribution of NDVI trends’ slopes during the conflict period (2002–2008) (A) and during post-conflict period (2008–2018) (B)

In conclusion, there are two issues that stand out from this descriptive analysis: (a) many areas in the Northern region have become ‘greener’ and (b) the standard deviation of NDVI trends within each sub-region has shortened.

First, in relation to the ‘greening’ of the environment in Northern Uganda, we consider that two drivers might be explaining this. Studies conducted around our second period of analysis (2018) show that agricultural land has been expanding in the region, sometimes in detriment of woodlands and forest (7, 15, 22). Agricultural land has increased, particularly in West Nile and Karamoja (15). Various policies and interventions put in place by the government of Uganda to promote and support farming in the Northern region aiming at ‘boosting agriculture through provision of inputs like improved seeds and seedlings, hoes, tractors and ox ploughs, among others’ (22, page 353).

Second, the shortening of the variation of NDVI trends means that extreme cases of positive-negative trends became more evenly distributed across space in the Northern region. We suggest this could be explained by a more equal distribution of vegetation growth/deterioration, compared to previous unequal geographies of environmental change during the armed conflict.

Based on the literature reviewed, our proposition to explain this is that the relocation of people from IDPC back to their lands and the expansion of economic activities in the Northern region during post-conflict meant a de-concentration of resource exploitation, the degradation of previously preserved areas, the restoration of vegetation in conservation sites, and the expansion of agriculture or other types of vegetation growth (e.g. grasslands, planted forests, etc.).

In addition, the expansion of infrastructure and urban centres (including refugee camps) might be explaining hotspots of vegetation deterioration.

Vegetation and Environmental Change at Sub-regional Level

Our spatial focus of analysis now turns to the four selected sub-regions and their districts: West Nile, Acholi, Lango, and Teso. For further discussions about vegetation change at district level, see Nardi & Runnström (2024).

West Nile Sub-region

West Nile sub-region stands out because mean NDVI trends in the conflict period (2002–2008) were negative in all its districts (except for Adjumani and Moyo that show no changes) and this was reversed in the post-conflict period when all the districts show positive mean NDVI trends (Figure 2). We propose that the ‘greening’ trend in West Nile might be attributed to the conversion of degraded forestlands to crop lands and the shift from subsistence to commercial/plantation farming.

Negative NDVI trends (shown in red) during the conflict period might be attributed to forest degradation. The boom in smoked fish trade between 1990 and 2000 resulted in overexploitation of forests for fuel wood, leading to a loss of over 70% of forest cover along the Nile during that period (15). But other drivers might explain the ‘redness’ of West Nile before 2002, such as population growth, including the influx of refugees into camps, which greatly contributed to resource extraction and vegetation deterioration (23), particularly in woodlands of Adjumani and Moyo districts (16). However, both districts showed an increase in vegetation activity in the post-conflict period of analysis. The discovery and exploration of oil and gas in the Albertine rift has also negatively impacted natural vegetation albeit more localised in West Nile.

We propose that deterioration of woodlands and forests due to resource extraction for fuel and housing might be explaining the ‘redness’ of West Nile in the conflict period 2002-2008.
Conversely, the greening of the sub-region until 2018 might be attributed to increased agricultural area.

Figure 2: West Nile sub-region, Uganda. Spatial distribution of NDVI trends during conflict (2002–2008) (right) and post-conflict (2008–2018) (left). NDVI trend statistics (below)

Acholi Sub-region

This sub-region shows dissimilar trends at district level. We propose that the negative NDVI trend in some areas after the conflict might be explained by the conversion of natural vegetation – restored during the armed conflict – to agricultural land or urban land use, which also increased between 1996 and 2013 in Acholi.

As the general trend, Acholi sub-region shows a decrease in extreme cases of vegetation deterioration/growth at district level.

Research has observed notable changes in land use and cover between 2006 and 2016 in some parts of Acholi (Aswa iii sub-catchment) where woodlands decreased, small-scale farming increased, while grasslands remained the dominant vegetation during the period until 2018 when agriculture and grassland were evenly distributed in all the area under study (22). Commercial large-scale agriculture has also increased in this sub-region during the post-conflict in Nwoya and Amuru districts between 2009 and 2019 (8).

Acholi sub-region – together with West Nile – is the main charcoal producer in Northern Uganda (10). The sub-region has a comparative advantage over other areas of Uganda for charcoal production because vegetation has been preserved during the armed conflict (24).

Acholi stands out for the increase in urban land between 1996 and 2013 (15). Urbanisation might explain hotspots of vegetation degradation in Acholi during the post-conflict period.

In conclusion, we propose that agriculture might be one of the central drivers explaining the greening of the natural environment in Acholi sub-region, over areas previously degraded, and logging and grassland degradation seem to explain vegetation degradation in areas previously restored and/or preserved during the conflict.

Figure 3: Acholi sub-region, Uganda. Spatial distribution of NDVI trends during conflict (2002–2008) (right) and post-conflict (2008–2018) (left). NDVI trend statistics (below)

Lango Sub-region

South of Acholi sub-region, Lango accommodated IDP by hosting sixty-one camps all closed by 2009 (UNHCR, 2009). We propose that the mean NDVI increment observed in different districts in Lango might be explained by the increase of land for agriculture and/or grassland as already observed others for the first decade of the conflict (4).

The statistical analysis shows that mean NDVI trend in the post-conflict period becomes much shorter in terms of variation in the increase/decrease of photosynthetic activity, which means that vegetation deterioration/growth becomes more evenly distributed in the sub-region (Figure 4).

During the post-conflict period, most of the districts show positive mean NDVI trends (except for Otuke). Dokolo stands out during the post-conflict because the majority of the surface of the district shows positive NDVI trends. In this district can also be found the highest positive mean NDVI trend of the sub-region. Based on secondary data, we consider that these tendencies might be explained by (a) expansion of agricultural land and forest regeneration or afforestation (e.g. 2099 ha of Kachung Forest Project) in the case of Dokolo (25) and (b) negative change in woody cover (e.g. Otuke) (26).

Figure 4: Lango sub-region, Uganda. Spatial distribution of NDVI trends during conflict (2002–2008) (right) and post-conflict (2008–2018) (left). NDVI trend statistics (below)

Teso Sub-region

Ten years ago, ACCS (2013) observed that Teso not only has experienced numerous armed conflicts but also cattle raids, which greatly impacted vegetation (natural and agriculture). Together with Karamoja, this sub-region is currently suffering from drought and floods that have destroyed crops, increased food insecurity and emigration (7).

During the conflict period (2002–2008) mean NDVI trends were positive for all districts in the sub-region, with some districts in particularly standing out due to the high mean positive NDVI trends. In the post-conflict period positive trends remained for all the districts (but Budaka, which showed a negative trend (Figure 5).

We propose that the positive NDVI trends in Teso might be explained by forest regeneration or afforestation. The ‘greening’ of Teso sub-region during the post-conflict period might differ from previous sub-regions studied as it seems to be forestland and not agricultural land that might be explaining this trend. Nevertheless, there are differences within the sub-region and statistical analysis shows that there is a tendency between both periods towards vegetation deterioration. In addition, similar to the other sub-regions, in the post-conflict period, the gap between vegetation deterioration-growth has shortened within each district compared to the conflict period 2002-2008. This means that there are not extreme cases of vegetation deterioration/growth.

Figure 5: Teso sub-region, Uganda. Spatial distribution of NDVI trends during conflict (2002–2008) (right) and post-conflict (2008–2018) (left). NDVI trend statistics (below)

Prospects for Sustainable Peace and Development

Our study has shown that some of the sub-regions and districts in Northern Uganda have been turning greener since the armed conflict. We have also proposed that this might be explained by the expansion of agriculture. However, other drivers might be at play. Indeed, forest restoration and/or expansion of woody cover and grassland, as in the case of Teso might be pointing to this.

The conservation of natural vegetation (grassland, forest) or previously degraded areas to agriculture crops might be indicating that the region has not been turning more biodiverse rich during the post-conflict. If the greening of Northern Uganda is explained by agriculture expansion, then we propose that there has been environmental deterioration to a certain degree, as agriculture implies the loss of wildlife habitats and biodiversity erosion. While agriculture might be conducive for food security and economic growth, the way it is organised and articulated with the natural vegetation is central for its sustainability, as well as for an equal development. If agriculture is motorised by large-scale monoculture of industrial crops in detriment of small-scale family-oriented crops and/or expands over forest and woodlands, biodiversity might be compromised along with ecosystem services central for local populations, for climate change mitigation and adaptation. Further research is needed to properly understand positive trends in vegetation activity (e.g. ‘greening’) as well as the impact of agriculture on biodiversity (e.g. use of agrochemicals and water and soil pollution).

The study has also shown that the geographical scale of vegetation change (degradation and restoration) during peace times has changed compared to conflict times and in different scales. Our NDVI study during the armed conflict and during the post-conflict shows that the geographical distribution of vegetation deterioration and growth has become more equally distributed in all sub-regions studied at the district scale of analysis. In this sense, Northern Uganda’s unequal geographies of environmental change have transformed. While it is possible to argue that vegetation is not further depleted during peacetime, it is also the case that vegetation is no longer being restored in the same intensity as during conflict time at regional scale. This should be further corroborated on the ground to properly understand the drivers. However, it is important to consider how scale matters here. Hotspots of deterioration (e.g. refugee camps or forest encroachment) can be observed if we use another geographical scale of analysis than the one used in this study (focused on sub-regional and district level). Future studies could look into other scales of vegetation and environmental change (sub-counties or parishes level).

What might these regional and sub-regional trends and possible explanations be indicating in terms of sustainable peace and development in North Uganda? If we understand agriculture expansion, along with infrastructure expansion, as signs of ‘progress’ and ‘economic growth’ we might conclude that Northern Uganda is undertaking processes of ‘development’ during the post-conflict period of analysis. However, it is important to question whether this development is sustainable and inclusive as well as the implications for peacebuilding. The management of natural resources during post-conflict peacebuilding should be carefully monitored in order to promote conflict-sensitive development and avoid resuming (armed) conflicts.

Our explicative analysis based on secondary data shows that environmental concerns and conflicts in the region in the post-conflict period of analysis might be related to the extensive use of land for agriculture, encroachment over wetlands and local forests, which might be indicating the unsustainability of this development model. While the local population continues to meet their fuel demands on biomass (charcoal and firewood), and their food needs on subsistence cultivation, environmental degradation will continue to play a key role in the sustainable development of the region as local communities are highly dependent on their natural environment for their livelihoods. At the same time, the expansion of large-scale industrial agriculture (e.g. sugar cane), oil exploration and exploitation or hydropower or carbon offsetting projects driven by corporations might further fuel land and environmental conflicts with local communities, as recently shown by environmental defenders in Northern Uganda. This – we propose – might weaken peace consolidation in the region, irrespectively of the ‘greening’ tendencies we observe during the post-conflict period of analysis (2008–2018) in some parts of the region.

Policy Implications

We suggest that future development policy should continue to have a particularised approach to Northern Uganda as peace is not yet consolidated. We propose that future research on vegetation and environmental change in Northern Uganda pays careful attention to dynamics of LULC on the ground and the implication of these uses and changes in natural resource exploitation and management. Our NDVI study could serve as a starting point to identify at local level processes of vegetation restoration and deterioration worth observing.

References

(1) Bruch C., Batra G., Anand A. with Chowdhury, S. & Killian, S. (Eds.), (2023). Conflict-sensitive conservation. Routledge.

(2) Brusset E. (2016). Evaluation of the environmental cooperation for peacebuilding programme. Post-conflict and disaster management Branch (PCDMB), United Nations Environment Programme.

(3) ACCS. (2013). Northern Uganda Conflict Analysis. Advisory Consortium on Conflict Sensitivity: Refugee law project, Safeworld & international alert.

(4) Nampindo S., Picton-Phillipps G., Plumptre A. (2005). The impact of conflict in Northern Uganda on the environment and natural resource management. USAID and Wildlife Conservation Society.

(5) GoU. (2015). The peace, recovery and development plan 3 for Northern Uganda (PRDP3). July 2015-June 2021. Republic of Uganda.

(6) Branch A. & Martiniello G. (2018). Charcoal power: The political violence of non-fossil fuel in Uganda. Geoforum, 97, 242–252. https://doi.org/10.1016/j.geoforum.2018.09.012

(7) NEMA. (2019). National state of the environment report 2018-19. National Environment Management Authority, Government of Uganda.

(8) Luwa J. K., Bamutaze Y., Mwanjalolo J. G. M., Waiswa D., Pilesjö P., Mukengere E. G. (2020). Impacts of land use and land cover change in response to different driving forces in Uganda: Evidence from a review. African Geographical Review, 40(4), 378–394. https://doi.org/10.1080/19376812.2020.1832547

(9) Serwajja E., Kisira Y., Bamutaze Y. (2024). ‘Better to die of landslides than hunger’: Socio-economic and cultural intricacies of resettlement due to climate-induced hazards in Uganda. International Journal of Disaster Risk Reduction, 101, Article 104242. https://doi.org/10.1016/j.ijdrr.2024.104242

(10) Haysom S., McLaggan M., Kaka J., Modi L., Opala K. (2021). Black gold. The charcoal grey market in Kenya, Uganda and South Sudan. Global Initiative Against Transnational Organized Crime.

(11) World Bank. (2018). Rapid assessment of natural resources degradation in areas impacted by the south Sudan refugee influx in Northern Uganda. Technical Report, International Bank for Reconstruction and Development/The World Bank and FAO.

(12) Olanya D. R. (2014). Asian capitalism, primitive accumulation, and the new enclosures in Uganda. African Identities, 12(1), 76–93. https://doi.org/10.1080/14725843.2013.868672
(13) Serwajja E. (2014). An investigation of land grabbing amidst resettlement in post-conflict Amuru district, Northern Uganda. [PhD thesis, University of the Western Cape].

(14) UBOS. (2021). 2021 statistical abstract. Uganda Bureau of Statistics.

(15) Li J., Oyana T. J., Mukwaya P. I. (2016). An examination of historical and future land use changes in Uganda using change detection methods and agent-based modelling. African Geographical Review, 35(3), 247–271. https://doi.org/10.1080/19376812.2016.1189836

(16) GoU. (2015). State of Uganda’s forestry 2015. Report. Ministry of Water and Environment.

(17) UBOS. (2021). Uganda national household survey 2019/2020. Uganda Bureau of Statistics.

(18) Ochola D. (2021). Black gold: Illegal logging for charcoal wipe out rare trees in Northern Uganda. Online news. Zenger News. https://www.zenger.news/2021/06/07/black-gold-illegal-logging-for-charcoal-wipe-out-rare-trees-in-northern-uganda/ (Accessed 02 12 2022).

(19) TNH. (2015). Charcoal boom a bust for forests. Online news. The New Humanitarian. https://www.thenewhumanitarian.org/report/94810/uganda-charcoal-boom-bust-forests (Accessed 02 12 2022).

(20) Mugizi F. M. P., Matsumoto T. (2021). From conflict to conflicts: War-induced displacement, land conflicts, and agricultural productivity in post-war Northern Uganda. Land Use Policy, 101, Article 105149. https://doi.org/10.1016/j.landusepol.2020.105149

(21) MWE. (2016). State of Uganda’s forestry. Ministry of Water and Environment, Government of Uganda.

(22) Oguzu B., Egeru A., Nyeko M., Obia A., Barasa B. (2018). Land use/cover change in Aswa III sub-catchment, Northern Uganda. RUFORUM Working Document Series, 17(1), 349-356.

(23) Hughes R., Owen M., Verheijen L., Kasedde C., Oule H., Begumana J., D’Aietti L., Gianvenuti A., Jonckheere I., Kintu E., Lindquist E., Tavani R., Xia Z. (2020). Rapid assessment of natural resource degradation in refugee impacted areas in Northern Uganda. Technical Report June 2019. International Bank for Reconstruction and Development, Food and Agriculture Organization of the United Nations, and World Bank.

(24) Kaguta V. (2022). Failed implementation of the reforestation policies depleting forest cover in Northern Uganda. Online news. New Vision. https://www.newvision.co.ug/category/news/failed-implementation-of-the-reforestation-po-132700 (Accessed 02 12 2022).

(25) Edstedt K., Carton W. (2018). The benefits that (only) capital can see? Resource access and degradation in industrial carbon forestry, lessons from the CDM in Uganda. Geoforum, 97, 315–323. https://doi.org/10.1016/j.geoforum.2018.09.030

(26) Ojok O. (2020). Why we must act to protect our Shea trees. Opinion. Nile Post. https://nilepost.co.ug/2020/11/12/why-we-must-act-to-protect-our-shea-trees/ (Accessed 01 07 2023).

October 28, 2024

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Our participation in the ACCESS Forum 2024 – Academic Collaboration Chile – Sweden in Stockholm

Theme 12: Territories and Commons in the Global North and South: An Intersectional Look at Forests, Land, Water and Bodies

Maria Andrea Nardi – Sandra Fernández – Felipe Maurelia Burgos – Hanna Ekström – Jacquline Boldt Corvalán – Katia Valenzuela-Fuentes – Marien González-Hidalgo – Marcelo José Becerra Parra – Noelia Carrasco Henríquez – Pamela Andrea González Fuentes – Pamela Bachman-Vargas – Paulina J. Pavez – Stefanie Pacheco-Pailahual – Yahia Mahmoud

Introduction

The Research Theme aims to contribute to unraveling the complex relationships between territories and commons in current extractivism frontiers. We welcome research on contemporary issues equally affecting Chile and Sweden around the extractive economy. We invite researchers interested in the current expansion of the extractive production model in South America and the Artics from a critical environmental approach.

We are interested in looking at the impacts of the extractivism in its manifold’s forms (mining, large-scale monoculture, etc.) on forests, land, water and bodies but also the contestations, resistances, and alternatives against it, from approaches ranging from critical theories on development and political ecology to those that draw on decolonial and feminist perspectives on post-development.

Expectations

Privileging an intersectionality as a research analysis tool this Research Theme called for researchers interested in discussing on some of the following questions:

●      The relationship between the extractivist model and socio-biodiversity degradation and violence. Plantations of exotic species and agroindustry are presented as the triggers of the loss of biodiversity, long periods of drought, contamination of soil and water, as well as the weakening of farmers, peasants, and indigenous economies. Mining, mineral and gas exploration disrupt herding, local cultures, and their relations with their natural environment. What is the relation between the extractive economy, socio-biodiversity degradation, and (slow) violence?

●      Global production chains motorising extractivism emerge in particular geographies of the Global North and South (e.g., urban areas) reshaping territories and commons in ‘marginal’ spaces (e.g., indigenous lands, urban peripheries). How can a decolonial approach assist us to better understand new colonial relations (global, internal, economic, political, ecological) in the world economy and its materialisations in territories and bodies?

●      Large-scale forestry and agricultural monoculture or metal and fossil fuel exploitation represent a plundering of natural common goods (such as soil, water, or minerals) and deepens the sexual and spatial division of labour. Women see their subsistence threatened since they have a central role in the management of natural resources and ecosystem services. In some spaces, they are forced to enter precarious salaried work which violates their own bodies-territory. Despite this, women manage to develop different ways of relating to nature through innovative agricultural, agroecological, governance practices of water, forests and soils. How can these practices allow us scholars to envision the potential of building decolonizing paradigms of development through the collective work of rural women (and men) (and together with them) in the identification of other ways of living on Earth and valuing nature and socio-cultural relations?

Our common ground

This synthesis is the result of three days discussions between scholars from diverse disciplines, coming from diverse territories both in Sweden and Chile, with very rich research and teaching experiences.

These discussions were facilitated by a variety of alternative and engaging methods. Such methods permitted an intellectual and embodied praxis that we share here with you.

While we acknowledge that common goods and spaces play a central role in the wellbeing of human and more-than-humans (“nature”), we observe that current capitalist development model radically transforms landscapes, territories, and bodies of those who inhabits ‘sacrifice zones’, in particular.

Not all of us who inhabit planet earth experience and suffer transformations equally. However, we observe that extractives economies exist both in Chile and Sweden, for example in territories of Sami or Mapuche peoples, in urban residential areas, in forests and waterscapes and beyond.

There is widely documented evidence that extractivism radically undermines balanced socio-ecological relations. We can see this in current climate change and biodiversity loss among other crises.

Nevertheless, such transformations do not go uncontested. From a diversity of territories peoples are resisting, organising alternatives to development, mobilising more pluricentric (and less anthropocentric) economies of production and reproduction.

We see therefore a need to rethink development models and those scientific knowledge systems that legitimise extractivism even when it is in the name of ‘sustainable development’

Science is not impartial, it is not neutral, it is not apolitical. What science do we need so that we can protect, defend, and restore our common goods and spaces?

How should we generate knowledge in a way that would allow us to challenge both development and science as we know it?

We call for an embodied and situated knowledge production that challenges the ‘scientific method’, this means to decolonise our epistemological and methodological ways of doing science.

We need more ethical, dialogical, horizontal and participatory knowledge production beyond academia.

ACCESS Forum has been for us an opportunity to create scientific community that thinks, feels, and produces otherwise.

One of the highlights of the Forum was the visit of Gabriel Boric – president of Chile – with his delegation. Ministry of Economy – Nicolas Grau – talked to us about forest in the country and we had the chance to discuss about the importance of considering environmental consequences of large-scale forestry in addition to working conditions in the sector.

Participants in Theme 12

Maria Andrea Nardi – Lund University, Sweden

Sandra Fernández – University of Concepción, Chile

Felipe Maurelia Burgos – Universidad de La Frontera, Chile

Hanna Ekström – Lund University, Sweden

Jacquline Boldt Corvalán – University of Concepción, Chile

Katia Valenzuela-Fuentes – University of Concepción, Chile

Marien González-Hidalgo – Swedish University of Agricultural Sciences, Sweden

Marcelo José Becerra Parra – University of Concepción, Chile

Noelia Carrasco Henríquez – University of Concepción, Chile

Pamela Andrea González Fuentes – University of Concepción, Chile

Pamela Bachman-Vargas – Umeå University, Sweden

Paulina J. Pavez – Universidad de Chile, Chile

Stefanie Pacheco-Pailahual – Universidad de La Frontera, Chile

Yahia Mahmoud – Lund University, Sweden

More information about ACCESS Forum 2024 in Stockholm here.

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Nuevo proyecto de investigación: Defensores y defensoras ambientales de derechos humanos – agentes de cambio en el nexo entre el cambio climático, la biodiversidad y la conservación cultural

Defensores y las defensoras ambientales en diferentes partes del mundo luchan por sus derechos políticos, culturales, sociales, económicos y ambientales, a menudo enfrentando intimidación y violencia por su trabajo y activismo. En este proyecto interdisciplinario, buscamos investigar en qué medida defensores y defensoras ambientales actúan como agentes de cambio tanto en la conservación cultural y de la biodiversidad, como en la mitigación y adaptación al cambio climático.

Primero desarrollamos una comprensión conceptual acerca de quienes son defensores y defensoras ambientales. Esto nos permitirá identificar dichos sujetos en diferentes contextos sociales y geográficos. Luego centramos nuestro análisis en Colombia, donde – luego de la firma del acuerdo de paz entre el gobierno y la FARC – defensores y defensoras ambientales han asumido un papel prominente pero precario como agentes de cambio. Analizamos sus objetivos, motivaciones y discursos subyacentes, y luego investigamos las prácticas que aplican para proteger el patrimonio cultural y promover un desarrollo sostenible. Analizamos más a fondo los efectos que tienen estas estrategias, tanto los éxitos como los obstáculos, incluidas las amenazas y su impacto en la vulnerabilidad de los defensores y las defensoras ambientales.

Durante el proceso de investigación, utilizamos un enfoque interdisciplinario basado en métodos mixtos provenientes de las ciencias políticas, la geografía humana, las ciencias de la sostenibilidad y el derecho. Nuestros hallazgos proporcionarán múltiples perspectivas acerca del nexo entre patrimonio cultural, biodiversidad y cambio climático. Con estos hallazgos, buscamos contribuir a una mejor comprensión y conocimiento para dar apoyo a diferentes grupos de defensores y defensoras, responsables políticos, organizaciones de la sociedad civil y académicos internacionales, tanto en Colombia como en Suecia.

Defensa del territorio y cuidado del ambiente en contextos urbanos y peri-urbanos

Lago del Cabrero, Cartagena de Indias, Colombia.

Uno de nuestros casos de estudio se centra en contextos urbanos y periurbanos del Caribe Colombiano. Desde allí miramos como diferentes sujetos defienden su territorio a la vez que cuidan la naturaleza en la ciudad de Cartagena.

En esta ciudad la cuestión ambiental se torna central para comprender los motivos y estrategias que diferentes sujetos utilizan tanto para restaurar la biodiversidad como para luchar por sus derechos.

La Ciénaga de la Virgen y de Juan Polo es territorio en disputa entre la contaminación y el cuidado ambiental, entre la reproducción de los medios de vida y la recreación, el ocio y turismo.

En este caso de estudio nos preguntamos:


• ¿Quienes defienden y protegen la naturaleza en la ciudad de Cartagena, en particular, en la Ciénaga de la Virgen y de Juan Polo?
• ¿Cómo se manifiesta esta defensa de la naturaleza en tanto defensa del territorio?
• ¿Cómo se articulan defensa y cuidado de la naturaleza en los diferentes espacios habitados y vividos en la Ciénaga de la Virgen y de Juan Polo?

Contacto: Maria Andrea Nardi, Sandra Valencia.

Defensa del territorio y cuidado del ambiente en contextos rurales

Cruzando el canal del dique de Pasacaballos a Barú. Cartegena de Indias, Colombia..

Otro de nuestros casos de estudio en el Caribe colombiano se enfoca en el territorio del Canal del Dique. Desde allí miramos a las comunidades negras, afrocolombianas y palenqueras como sujetos luchando por sus derechos ancestrales en el marco de la justicia restaurativa.

En esta eco-región la cuestión socio-ecológica se torna central para comprender los motivos y estrategias que diferentes comunidades locales y sus organizaciones utilizan tanto para restaurar sus ecosistemas como para luchar por sus derechos.

El canal del dique – declarado territorio víctima por la Jurisdicción Especial para la Paz en noviembre de 2024 – disputa su identidad entre territorio de vida de vida múltiples comunidades de pescadores y pescadoras, campesinos y campesinas e indígenas y los proyectos de infraestructura para mejorar la navegabilidad de grandes buques transportadores de hidrocarburos, metales y agricultura industrial.

En este caso de estudio nos preguntamos:

  • ¿Como defienden y protegen la naturaleza en su territorio las comunidades que hacen parte del Canal del Dique?
  •  ¿Cuáles son las amenazas actuales que sufre el territorio y cuáles son las históricas?
  •  ¿Qué tipo de estrategias utilizan las comunidades en la defensa de sus espacios de vida?
  • En particular, ¿cómo se utilizan los diferentes marcos legales y el litigio? ¿Qué significa para las comunidades afectadas la declaración de la JEP del Canal del Dique como territorio víctima?

Contacto: Maria Andrea Nardi, Britta Sjöstedt, Sandra Valencia.

Acerca del proyecto

Fecha de comienzo:  01 de marzo de 2023

Fecha de finalización: 28 de febrero de 2027

Colaboración: Universidad de Lund (LU), Instituto Raoul Wallenberg de Derechos Humanos y Humanitario (RWI).

Financiamiento: Consejo Sueco de Investigación para el Ambiente, las Ciencias Agrícolas y el Planeamiento Espacial (FORMAS).

Investigadores e investigadoras miembros

Krause, Torsten. Centro de Estudios de la Sustentabilidad (LUCSUS) (LU). Director del Proyecto.

Ituarte-Lima, Claudia. RWI.

Valentina Lomanto. LUCSUS. Estudiante de doctorado.

Nardi, Maria Andrea. Departamento de Geografia Humana (LU) y RWI.

Sjöstedt, Britta. Facultad de Ciencias Jurídicas (LU).

Valencia, Sandra. RWI.

Zelli, Fariborz. Departamento de Ciencias Políticas (LU).

Algunos resultados del proyecto

Samper, J. A., & Krause, T. (2024). “We fight to the end”: On the violence against social leaders and territorial defenders during the post-peace agreement period and its political ecological implications in the Putumayo, Colombia. World Development, 177. https://doi.org/10.1016/j.worlddev.2024.106559

Ituarte-Lima, C., Nardi, M. A., & Varumo, L. (2023). Just Pathways to Sustainability: From Environmental Human Rights Defenders to Biosphere Defenders. Environmental policy and law, 53(5-6), 347-366. https://doi.org/10.3233/EPL-239009

In English here.

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How do local peoples’ natural environments matter for peacebuilding and human rights? Nature beyond natural resources

Entering the Northern region of Uganda crossing the Victoria Nile on the way to Gulu from Kampala. Photo: Maria Andrea Nardi, 2014

Maria Andrea Nardi

There is consensus that access to (and enjoyment of) a healthy environment, biodiversity and natural resources is central for the fulfilment of various human rights (e.g., food, water, or shelter). Conceptual and legal connections are usually done between economic, social, and cultural human rights and the natural environment by considering the importance of biodiversity and natural resources’ exploitation in people’s livelihoods and cultural reproduction. However, I argue, there are many other roles ‘nature’ can play in consolidating sustainable peace and human rights.

In post armed conflict settings, with the urgent need to attend gross human rights violations and set up the reconstruction of the economy and state institutions, there is a general tendency to consider the natural environment either as resources to be exploited or as space to be territorialised to facilitate this process (e.g., building communication infrastructure).

In Northern Uganda the natural environment seems to be far much more important than as mere provider of resources for post-conflict peacebuilding. Based on a preliminary literature review and online interviews with local stakeholders, I look into the role that the natural environment or ‘nature’ plays for communities in Northern Uganda. I focus on those roles that I consider to be relevant to fostering sustainable peace and human rights in conflict affected areas.

The natural environment in Northern Uganda beyond natural resources and biodiversity

As discussed in an earlier post in this blog, over a long period of time Northern Uganda has been the scenario of war between two armed parties: the Lord Resistance Army (LRA) and the Uganda People’s Defence Force (UPDF) (Government of Uganda) particularly around Acholi sub-region (or Acholiland). Peoples and nature found themselves in the middle of a violent conflict, which consequences are still felt today.

In looking into what kind of conflicts arose during peace time and how local communities heal and recover after two decades of violence, I found three issues that stand out in relation to the natural environment and how nature could be conceptualised beyond ‘natural resources’. In the following sub-sections, I give a closer look at them: (a) nature as a semiotic system, (b) nature as medicine for the soul, and (c) nature as public space.

Nature as semiotic system

In Northern Uganda, once people start moving out of internal displaced camps (IDC) and resettling ‘back home’, evidence shows that conflict among families and clans arose due to access to land. One of the diverse explanations about land conflict relates to the change in the natural environment, the disappearing of features in the landscape that used to serve as markers for territorial formations. The war took these natural markers with it. According to OHCHR:

“In northern Uganda almost all land, particularly in rural areas, is owned under customary tenure as first recognized by the 1998 Land Act. Accordingly, land is owned without any form of documentation, ownership being based on previously accepted settlement on a plot of land and use thereof. Land boundaries are equally not surveyed nor recorded in any way. Boundaries are, however, known to the members of the communities and marked with natural features, including trees and field refuse” (1).

The natural environment plays a central role in people’s everyday life as a semiotic system. This means that different people give different meanings to rivers, ponds, stones, trees, etc. In this sense, the biophysical world can be a powerful means to anchor -but also allow movement of- individuals and groups across space and time.

Different elements of the natural environment (from a river to a stone) can be powerful markers. These elements have a semiotic purpose: they assist people in navigating their surroundings, their ‘environment’. A mango tree at a crossroad, a stone on the right side, two strings of water intersecting, a pond by the left of the road, among other, can be used by local peoples to sign the way to reach somewhere, to move around, to find their way. When land ownership is based on customary tenure and no boundaries are set by formal demarcation systems, peace between families, communities, clans depend on these landscape markers (2).

What happens then when these markers are gone? When in 2007 people started returning to their family or ancestral lands, in many cases they could not recognise those lands they used to cultivate, use for hunting or gathering, grazing animals, or performing spiritual rituals. Those trees, stones, waters, even graves, that once helped people demarcate their parcels and navigate their surroundings were no longer there. A decade-long life in IDC made burials completely different from the past. Family graves, once powerful markers in the landscape to claim land rights due to ancestry, were gone, and with that the possibility to access and secure land (3).

Looking into districts and sub-regions boundaries conflicts in post-conflict Karamoja and Teso, Bainomugisha et al. (2007:12) provide a telling narrative about the relevance of the natural environment and landscape in territorial formations for local peoples:

The Acacia tree: The boundary between Karamoja and Teso? 
(Photo by Ngoya J.B.) 
Source: Bainomugisha et al. (2007: 19),

“… the Acacia tree marks the border line between Katakwi and Moroto districts and has a milestone that runs through to Sising hill and bares a straight line up to Lotukei Mountain. Also, along the same axis can be traced the old mark of signposts which were inscribed South of Karamoja in 1963. These border marks can be found adjacent to the same acacia tree and during the dry season, the straight lining can be seen from above in an aerial view”. (4)

“The Acacia tree: The boundary between Karamoja and Teso? (Photo by Ngoya J.B.)”. Source: Bainomugisha et al. (2007:19).

Nature as medicine for the soul and social bonding

The Agreement on Accountability and Reconciliation signed in 2007 between the Government of Uganda and the LRA clearly defined four different traditional rituals performed by the Iteso (Ailuc), the Langi (Kayo Cuk), the Acholi (Mato Oput) and Madi (Tonu ci Koka) “to reconcile parties formally in conflict, after full accountability”.

Cleansing and reconciliation rituals play a key role in Acholi culture. After the war, there was a desperate need for reconciliation between civilians and abductees (ex-combats), a need to welcome them back, a need to heal from distress that is still felt today (5).

Mato Oput is probably the ritual most written about. It is a reconciliation ceremony that takes place after a killing of someone from a friendly clan (6). The term refers to the drinking of oput, a bitter drink prepared with smashed roots of the Oput tree and drunk at the pick of the ceremony. Some consider that “there is perhaps no single tree more vital in the great work of healing from the brutal civil war that has raged throughout Acholiland for over twenty years” (7).

In fact, Joseph Wasonga tells that when in 2003 Museveni – Uganda’s president – referred to the situation in the north of the country to the International Criminal Court (ICC), he brought into light the fact that for many different stakeholders the local justice system should be in charge of the process of “mediation, trust building, acknowledgment of wrongdoing, compensation, reconciliation, and restoration” (8). Wasonga adds that:

“The principles and practice of mato oput are founded upon the Acholi belief that crime is essentially a violation of relationships in a community. Hence, mato oput can be instrumental in restoring broken relationships between victims and survivors and between perpetrators and the entire community. Ugandans continue to debate the capacity of mato oput as a mechanism for sustainable peace in the context of the intractable conflict in the north” (8).

The mato oput ceremony is the culmination of a long process of mediation. For the performance, not only parts of the Oput trees are needed but other elements from nature or the local natural environment.

Preparing for the Mapo Oput ceremony

Source: Flickr. Copyright © 2010 Justice and Reconciliation Project

There are other ceremonies and rituals associated with ‘traditional ways of coping with consequences of traumatic stress in Acholiland’ (6). Cleansing rituals are central in this process, and elements from the natural world such as tree branches or sticks, eggs, livestock, are necessary for ceremonial performances. Thomas Harlacher tells us that “the nyono tonggweno (“stepping on the egg”) and lwoko pik wang (“washing away the tears”) rituals have been especially important in the welcoming and initial cleansing of people who have returned to the community from the LRA war” (6).

In all these cases, the natural environment of local communities is relevant and necessary for accountability and reconciliation, for healing and sustaining peace.

Nature as public space

Finally, other issue that stands out in relation to the role of the natural environment for peacebuilding and human rights, is its function as public space.

In Uganda, as in many other places of the world, trees in villages are important spaces for reunion. Big or small trees provide shelter from the sun, thus people stay under their shade to cool down, to chat, to play, to read, to teach or study, even to discuss the future of the local community.

The public space under a tree might serve as an arena for political participation, empowerment, and social cohesion, for community healing and reconciliation.

A group of people gathered under a tree

Photo: C.C. Chapman, 2012, in Alamy Stock Photo

Some tree species are deemed sacred, and some ones (because of their size, shape or location) are considered worth of worship (as the Nakayima tree in central Uganda, which is considered a shrine).

As public space, the natural environment is central in the fulfilment of many different human rights, not only those related to a healthy environment. I am thinking here on those aspects of public space that are conduit to political participation, community development, social and cultural reproduction, among others.

Final comment: the natural environment in peacebuilding and human rights

Different cultures use and valorise nature and their environment in diverse ways. The natural world form part of local and global narratives and cosmologies and it is intrinsic in many aspects of everyday life.

A narrow understanding of nature that restrict people’s possibilities to relate to each other (relations among the different genders, age groups, clans, tribes, ethnic groups, etc.) can further create conflict either by marginalising certain socio-ecological knowledges or destroying the material base for peoples’ relations among themselves and with their environment.

In this context, the natural environment turns out to be a catalytic agent for human rights fulfilment, transitional justice and sustainable peace in ways that go beyond fair access and distribution of natural resources.

Acknowledgements

I extend my gratitude to those local stakeholders in Acholi who had shared with me their time to talk over Zoom or phone about their current interventions in the region to promote peace and sustainable development.

I am thankful to Amaranta Thompson, Marta Kolankiewicz, Riya Raphael, Vasna Ramasar, and Alice Kasznar Feghali for their feedback on an earlier draft of this blogpost.

This research is supported by the Swedish Research Council for Sustainable Development (FORMAS – Grant 2018-00453).

References

(1) OHCHR (2008). “Activities of the Office of the High Commissioner for Human Rights in Uganda. Annual report of the United Nations High Commissioner for Human Rights and reports of the Office of the High Commissioner and the Secretary General. Report of the High Commissioner for Human Rights and follow-up to the World Conference on Human Rights. Addendum.” A/HRC/7/38/Add.2 (paragraph 29).

(2) Kandel, Matt (2016). “Struggling over land in post-conflict Uganda”, in African Affairs 115(459): 274–295. https://doi.org/10.1093/afraf/adw001

(3) Meinert, Lotte, Willerslev, Rane & Seebach, Sophia (2017). “Cement, Graves, and Pillars in Land Disputes in Northern Uganda”, in African Studies Review 60(3): 37-57. doi:10.1017/asr.2017.119

(4) Bainomugisha, Arthur; Okello, Julius & Ngoya, John Bosco (2007) “The tragedy of natural resources dependent pastoral communities. A case of Teso-Karamoja border land conflict”, ACODE Policy Research Series 23. Advocates Coalition for Development and Environment, Kampala.

(5) Kasozi, Okot Benard (2019) “Fragile Resilience: “Post-Conflict” Environmental Battles in Northern Uganda”, in Refugee Law Project website. Refugee Law Project, Kampala.

(6) Harlacher, Thomas (2009). Traditional ways of coping with consequences of traumatic stress in Acholiland Northern Ugandan ethnography from a Western psychological perspective, PhD dissertation. Department of Psychology University of Freiburg, Switzerland.

(7) Moll-Rocek, Julian (2016). “Healing in Community: Three Acholi Plant Medicines”, in Wild Forest and Fauna website. https://wildff.org/healing-community-three-acholi-plant-medicines/

(8) Wasonga, Joseph (2009). “Rediscovering Mato Oput: The Acholi Justice System and the Conflict in Northern Uganda”, in Africa Peace and Conflict Journal 2(1): 27-38.

(9) Macdonald, Anna & Kerali, Raphael (2020) “Being Normal: Stigmatization of Lord’s Resistance Army Returnees as ‘Moral Experience’ in Post-war Northern Uganda”, in Journal of Refugee Studies 33(4): 766–790. https://doi.org/10.1093/jrs/fez117  

February 22, 2023

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Making a stand for memory and place

Credit: Juan Samper, 2021

In this blog post, Lund University Master student Juan Samper briefly summarises his thesis research in the Putumayo region of Colombia. The thesis is publicly available (link below).

Written by Juan Antonio Samper and Torsten Krause, Lund University

Five years into the present peacebuilding cycle in Colombia, violence is increasing again across the country, but particularly in rural areas that were also previously affected by the armed conflict. In the Putumayo department, conflicts between the state, armed groups and local communities persist. For decades the Putumayo has been the scene of social conflict between armed groups seeking control over strategic portions of land for narcotrafficking and military advantage. Since the peace agreement between the FARC-EP and the Colombian Government was signed in 2016, the violence between different armed groups, including FARC dissidents, and the Colombian armed forces as resurged, but increasingly as a socio-ecological conflict, centered around access to and control over land and natural resources.

One of the most horrific new manifestations of this wave of violence is the steep increase in threats, attacks and assassinations of social leaders who defend human and indigenous rights, and in many cases also the environment. In the Putumayo alone, more than 67 social leaders have been murdered since the peace agreement was signed in 2016. Many more have been victims of other types of aggressions or receive death threats continuously, forcing leaders to live in hiding or to flee to more secure localities. The reason behind these threats vary. Social leaders fight for the recognition and protection of their communities’ collective rights and ways of life, and they oppose armed groups and report their presence and activities to the authorities. Social leaders also support projects and processes connected to the peace agreement like the rural reform and substitution programs for illicit crops, mainly coca. In their own words, social leaders defend the territorities they are culturally and often spiritually connected to.

But who is a social leader? What is the defense of the territory? How do social leaders defend the territory? And what are the implications of the violence against social leaders for the defense of the territory? These are the questions that I set out to investigate in this ethnography supported by the Nature of Peace project.

I found that the key characteristics that determines who a social leader is, is the recognition of their roles by their social bases, the people they fight for and who they come to respresent. As for the defense of the territory, I found that it is a form of collective action that unites the place-based struggles of communities who share histories of marginalization and dispossession, who aim at improving their material conditions such as fighting poverty, accessing land and protecting the environment and human rights.

The role of social leaders in the defense of the territory is significant. They craft narratives and unite struggles while recognizing the differences and, particularly relevant in the pluricultural Putumayo, the tensions within the different ethnicities and social groups who inhabit these territories. Furthermore, they mediate between their communities and external actors (for instance the regional or national government), expose the interests and (in)actions of the latter, actively push for land redistribution and titling processes, and denounce violations of human rights and environmental degradation in their territories.

In the conclusion of my thesis, I argue that the implications of the violence against social leaders can be interpreted as the production of oblivion and detachment. These quintessential forms of political violence imply the invisibility and historical irrelevance that many communities have been subjugated to by imposed forms of development and armed conflict. Therefore, to protect social leaders is to protect collective memory and the attachment that communities in the Putumayo, and all around Colombia, have to their territories. The implications of this systematic silencing of social leaders in Colombia begs further investigating whose interests does the production of oblivious and detached communities serve, the extent to which transformative pathways to peace, democracy and sustainability are foreclosed with the silencing of social leaders, and the forms of resistance in defense of the territory that emerge in response.

Interested in reading the entire thesis? Click here (link to Lund University Library).

August 9, 2021

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Nature and Peace in Northern Uganda: using satellite data to assess environmental change in conflict and post-conflict areas

From the Kalongo, Northern Uganda. Source: https://www.dronestagr.am/from-the-kalongo-northern-uganda/

Micael Runnström & Maria Andrea Nardi

Nature is a key concept in our ongoing research, but we need to define it if we want to evaluate possible drivers of environmental conflict within the peace process. If nature is defined as green resources, for instance, it is possible to assess how vulnerable peace might be, against environmental changes occurring on the ground by using satellite data. Satellite data can then be used, in combination with fieldwork and interviews, to monitor and map changes in green environments in a post-conflict period.

As satellite data can be classified into land cover categories (e.g., forested area), it is possible to compare two land cover classifications representing different stages in time, and map changes that have occurred on the ground. To map changes in a whole country at high detailed resolution is however a tedious and difficult task that requires good understanding about the landscape, field ground truth, and also knowledge in how to prepare and process satellite data.

An alternative way is to use a calibrated and prepared satellite data time series of a product, e.g. a vegetation index (VI). A VI is constructed by measuring the difference in reflected solar energy between different parts of the electromagnetic spectrum, especially focusing on the red wavelength band (~0.65 µm) and the near infrared band (~0.75 – ~1.5 µm). A time-series dataset of VI can then be used to calculate trends through time.

One VI widely used is the Normalised Difference Vegetation Index (NDVI) which is an indicator of vegetation greenness of biomes. The NDVI is providing a physical status of leaf area index (LAI), fraction of vegetation cover, and fraction of absorbed radiation for the photosynthesis. These parameters provide a possibility to assess density, production and health of the vegetation (see here).

To monitor environmental changes in northern Uganda during and after the armed conflict around 2008, a time series of MODIS (Moderate Resolution Imaging Spectroradiometer satellite sensor) NDVI data at 1000*1000m pixel resolution between 2002 and 2018 was used to evaluate changes in vegetation properties. The annual phenology was analysed to discover the vegetation cycle inferred by NDVI values and rainfall pattern of Uganda.

In Uganda there are two main rainy seasons (March – May and September – November). NDVI images, acquired in June-July each year, provides an annual footprint of the vegetation peak that can be used to calculate the linear trend of the vegetation activity through the time series in each 1 km2 pixel.

By calculating the linear trend direction for two different periods it is possible to evaluate how vegetation have developed during the armed conflict period (2002 – 2008) (figure 1), compared to the post-conflict period (2008 – 2018) (figure 2). A negative trend of NDVI indicates that vegetation activity was declining (negative equation – red colours) and a positive trend indicates that the photosynthetic activity, and thus vegetation LAI or density was increasing (green colours). Yellow colours indicate that the trend line equation is close to zero meaning that vegetation activity was stable throughout the period.

Figure 1. North Uganda, sub-regions. NDVI trends in the conflict period (2002 – 2008)

Figure 2. North Uganda, sub-regions. NDVI trends in the post-conflict period (2008 – 2018)

NDVI trends can now be further analysed to derive statistics for different administrative regions and land use systems (e.g. national parks, forest reserves), in order to evaluate gain or loss of vegetation activity, inferred by NDVI.
We will expand on this in the coming post! Thanks for your comments and sharing our preliminary work, supported by the Swedish Research Council for Sustainable Development (FORMAS – Grant 2018-00453).

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Peace in the peaks? Reinforced Inequalities in the Colombian Andes during the Post-conflict

Las Hermosas - Colombia. Photo taken by Laura Betancur-Alarcón, 2019.

A new research article published in Frontiers in Environmental Science written by LUMES alumni Laura Betancur-Alarcón and LUCSUS researcher Torsten Krause portraits how the transition towards peace in Colombia is marked by changing land-uses and a new type of environmental conflicts between farmers and environmental authorities in the mountains of southwest Colombia.

“Do you see that fence behind my house? Two years ago, it was not there, but further up. In that space, I used to graze my cows. But when the guerrilla left and the landowners came back, they fenced the whole plot”

In this quote a peasant narrates why, with the withdrawal of the Revolutionary Army Forces of Colombia (FARC) from her village, one large landowner came back to his land in order to build several fences so that he could impose the boundaries of his plot. However, the return of the landowners restricted access to water and land for those peasants who do not have legal land titles in the region (which in rural Colombia is very common).

This particular testimony exemplifies how new dynamics in land and water access in the Las Hermosas region, a high Andean forest area in southwest Colombia, emerge after the peace agreement between the FARC and the Colombian state was signed in 2016. But what does the peace agreement and these new dynamics mean for those small peasants who do not have legal land titles? What are the conflict legacies that change in this post- agreement phase and which are the social consequences of recent ecological redistributions?

In the article, the authors describe the local dynamics shedding light on the transition between the rules previously imposed by the FARC and the State’s agencies attempts to re-introduce formal land and water governance mechanisms today, after the FARC has left the region as a result of the peace agreement.

The article highlights how peasants without land ownership experience less access to water and land after the FARC’s retreat due to the return of landowners, the legal arrangements about ownership of the land, the procedures for obtaining legal water concessions and the governmental decisions on water resource conservation. These tensions reinforce the historically unequal resource and land distribution that characterize Colombia and which.

As part of the Nature of Peace research project, the ethnographic study contributes to the ongoing discussion about water governance in post conflict settings by presenting evidence about the Colombian highlands, home to important mountain ecosystems that provide water to a large population and industry.

“The long-lasting influence the FARC had in these regions cannot be ignored when understanding the change in access to and use of lands when the state returns and enforces its laws in areas that were inaccessible for several decades because of the armed conflict”, says Laura Betancur.

This work was supported by the Swedish Research Council for Sustainable Development (FORMAS – Grant 2018-00453) and the fieldwork for this research was funded by the International Swedish Center for Local Democracy (ICLD). The full article can be found here.

October 29, 2020

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Environmental degradation, human rights and unsustainable peace in Northern Uganda

Credit: Charles Nambassi, in Pixabay

Maria Andrea Nardi

The armed conflict between 1986 and 2007 in Northern Uganda had profound impacts on human rights and on the degradation of the natural environment. Unfortunately, peacetime did not revert this. On the contrary, the consolidation of extractive supply chains is bringing environmental deterioration to another scale while social conflicts are emerging among ethnic groups, local communities, families, and authorities around land access and tenure.

In 2007, while the peace talks were going on, the UN High Commissioner for Human Rights made a number of recommendations to Uganda’s national authorities and the Uganda Human Rights Commission, including: “to ensure the integration of human rights and justice as key elements for sustainable peace” (1).

After the war, it has been claimed, the  Government of Uganda has made significant progress “to improve respect for human rights and the enjoyment of these rights by all individuals under its jurisdiction” (2) and to advance the “rule of law and democracy including ratification of key international and regional human rights instruments” (3).

Unfortunately, current environmental transformations in Northern Uganda are hindering that progress. Even though the rebels – the Lord Resistance Army (LRA) – are no longer active in the country, peace in the region is yet to be guaranteed.

Disputes over access to (and exploitation of) land and natural resources, as well as the resulting environmental degradation, are playing a key role in the future of peace in the eight sub-regions that make up the North region of the country.

In June 2020, I had a conversation with Patrick Okullo – journalist and environmental advocate based in Gulu, Acholi sub-region– and learned that during and after the war, environmental concerns were rising in the local agenda for peace. Unfortunately, this was not translated into an environmental peacebuilding policy. Journalists, NGO’s communities, and local authorities among others, are strongly advocating for environmental justice and human rights protection, for a sustainable peace in Northern Uganda.

In the following two sections, I share some of the key concerns we discussed with Patrick and complement with other sources such as those from local journalists and academic experts. In the final section, as a way of conclusion, I establish linkages between the protection of the natural environment and the protection, promotion, and fulfilment of human rights in the context of Uganda.

The emergence of ‘new’ natures and supply chains during war

For a period of about twenty years, Uganda witnessed its most prolonged armed conflict between a rebel army (LRA) and the national security forces – the Uganda People’s Defence Force (UPDF). Even though different sources contest the final number, in 2004 it was estimated that 1.4 million persons were pushed from their homes into internal displaced people’s camps (IDP camps) (4) in order to facilitate UPDF’s surveillance and securitize the most conflictive districts: those of Acholi sub-region (former districts of Gulu, Kitgum and Pader).

Patrick Okullo recalls that during the armed conflict, the Ugandan security forces arrived in the North to reach the LRA rebels seeking to deter their violence towards civilians and stabilise the situation. This was done by the construction of roads crossing forests and savannahs. In the process of implementing these strategies, natural resources were discovered by these actors coming from other regions of Uganda. Logging and trading of valuable tree species, such as the Africana Afzelia started then, when the security forces accessed unexplored forests. At the same time, they had access to natural resources in “abandoned” rural areas, as Patrick recalls:

“…in the process, when people were in the camps, when in [1996] they left their homes and  were confined in the camps, the security forces, the LRA and the UPDF they had access to these areas, they would exploit whatever they could in terms of natural resources, this contributed to degradation”.

Environmental and forest degradation started during war, with the emerging trend of logging of valuable species for trading, small-scale charcoal production and tree cutting for other purposes (such as building) for household consumption.

The high number of people living in camps resulted in an uneven spatial distribution of natural resources exploitation in the Northern sub-regions, highly concentrated in the camps and around them, as those living there “resorted to cutting of trees, for charcoal burning, for fuelling, for cooking. This also contributed to high level of degradation”, according to Patrick (see also 5).

In 2005, the USAID and the Wildlife Conservation Society sponsored a comprehensive study on the impact of the armed conflict on the environment and natural resources management in Northern Uganda (6). Based on mixed-methods and the use of remote sensing technology to study vegetation cover in the country, the report affirms that:

“In north eastern Uganda there has been a net loss of woodland (…). Around urban centres loss of woody cover was particularly high, although for Gulu and Kitgum this was confined to the immediate vicinity of the town and around IDP camps. Around Lira  there has been widespread loss of woody cover, which may be partly a result of the conflict (people migrating south) but also due to expanding human population and conversion of natural habitat to farmland” (6: 9-10). [*]

The paradox is, nevertheless, that the armed conflict worked also as a driver for environmental protection. The study shows that vegetation was also restored in some of those territories where the LRA rebels were based, or with no easy access. This might be explaining the higher level of environmental conservation: “[t]here is a large belt of increased woody cover west and north of Kitgum where the LRA has been most active and as a result it is clear that there has been some recovery of natural habitat as a result of the conflict” (6: 9).

The causes of vegetation change need to be further explored on the ground. The internal armed conflict has been a clear driver of vegetation change, but other factors might be explaining this, such as climate change or population growth (expansion of urban settings and/or farming land).

The report argues, however, that “it is clear that the movement of large numbers of people to IDP camps has allowed vegetation to recover in areas they have vacated and has led to degradation of vegetation around the camps and urban centres where they have settled” (6: 10). This explains the uneven geographical distribution of environmental degradation and conservation.

New conflicts and environmental deterioration during peacetime

Environmental degradation did not decrease after the armed conflict and during peacebuilding. On the contrary, it intensified. Savannahs and forests restored, turned into a source of rich timber to be exploited during peacetime. TNH (2012) observes that this is particularly the case because those regions previously supplying Kampala were totally depleted (7).

From 2007, once the violence against civilians deescalated and people started leaving the camps, Northern Uganda became the scene of the expansion of charcoal production and high-value timber extraction for distant markets such as those in Kampala, Kenya or China.

According to the Ministry of Water and Environment from Uganda (2016), during the period 2010-2015, an estimated number of 250,000 hectares of forest were lost. In the same period, forest estate outside protected areas reduced from 61% in 2005 to 38% in 2015 (8).

The resettlement process brought people back to their land, but with much need to complement their meagre incomes, as farming and husbandry take time to give a produce. Livestock had been wiped out from the region as a result of the war (9) so people had to restart their livelihoods. This partly explains the resulting land use change and ecological degradation that we are witnessing now.

Charcoal production and high-value timber species

During the post conflict and peacebuilding period, new and powerful actors arrived in the North and scaled up natural resource extraction and trade (10), not only for valuable timber logging but also for charcoal production.

This ‘industrial’ or large-scale charcoal production incorporated small-scale farmers and other rural dwellers into an international supply chain, highly extractive and dependent on natural resources, further marginalising local communities from their natural resources and livelihoods and/or inserting them at the bottom of emerging international supply chains.

Patrick Okullo explains that the levels of degradation and conflict intensified between 2015 and 2019: “hundreds of trucks would pass day and night from the Acholi sub-region and part of West Nile down South to Kampala”.

He further clarifies that trees such as shea nut or African Afzelia play an important role in the cultural life of Acholi people, who suffer in their territory much of the impacts of the armed conflict. This is why local chiefs, and other cultural institutions are worried to see how these trees are decreasing in number, as people will not only miss food and shelter, but cleansing rituals that are very important for the life in community, peace building and conflict resolution. Cultural leaders understood that failure to protect precious trees would affect in the future local peoples’ culture as these species have a key role in the reproduction of social life.

Access to land

New conflicts emerged during the post-conflict between local leaders, communities, clans, ethnic groups and families due to contested land ownership, district borders, soil degradation, land use change, over exploitation or access to local forests, among other issues related to the natural environment (11; 12).

Patrick Okullo recalls that “after the war the owners of those lands where camps were established were appealing to the government to support them, to compensate them, because the camps were established in their lands, and the natural resources were highly destroyed”.

The fragile land tenure and unstable land access pushed people to cut down trees as they were unsure for how long they would have access to natural resources. This has further accelerated the degradation process, according to different sources (10).

In this context, the arrival of investments for oil exploration and exploitation, and agribusiness –such as sugar cane or cattle ranching- has exacerbated conflicts between those supporting one or another livelihood and/or land use (13, 14, 15). Wildlife conservation in natural parks and reserves has also brought conflicts between local dwellers and authorities (16).

Role of the local district authorities

Local district authorities realised the need to address these urgent matters and understood – Patrick shares – that if tree cutting continues, acute weather changes would occur, affecting the soil humidity or quality and abundance of water and in the long term this will affect agriculture production, cattle raising, and other important livelihoods directly dependent on natural resources and ecosystem services (such as fisheries).

This explains that local district authorities for the entire Acholi sub-region came together and passed a bill in 2016 to control charcoal trade and the movement of timber from one place to another (17). This ordinance seeks to regulate the transportation of timber making it illegal to move it around without the corresponding documents from the authorities.

According to Patrick, “now that the authorities have been enforcing new control mechanisms, tree cutting is decreasing and less timber is leaving the region”. It seems at least, that illegal charcoal trade might be decreasing (18) though this is contested (19). In addition, “they are currently drafting a charcoal policy to address alternative sources of energy for households”, Patrick tells me.

Human rights and the environment: building sustainable peace

It has been argued by many that the armed conflict in Northern Uganda began as a consequence of the historical economic and political marginalisation of the region from the rest of the country (20). The armed conflict brought violence to people and to their natural environment, the violation of all kinds of human rights.  

Even though the armed conflict is over, peacetime unfortunately is not completely free of violence. Nowadays, violence against people continues in an indirect way: against their nature, their natural environment. It might not be exactly the same actors perpetuating it, but there is no doubt that the role of the Ugandan security forces is still relevant. As Branch & Martinello (2018: 242) put it “charcoal production, and its particular destructiveness, should be understood as a continuation of the violence of the 1986–2006 war between the Lord’s Resistance Army and the Ugandan government” as “[m]ilitarized, forceful displacements of communities by the state, whether for minerals, game reserves, parks, infrastructure, agri-business, or personal accumulation, are often enforced through military violence” (p. 248) (10).

Ecological degradation and environmental deterioration during the armed conflict was the result of the activity of few actors (e.g. army officials, camps dwellers) and it was very much localised (e.g. around the camps) (6). The geographical scale of environmental deterioration during peacetime has changed: it has increased. The network of stakeholders became more complex, bringing together diverse actors within and outside the Northern region (7, 10, 19).

It can be argued that peace succeeded in inserting the region in national and international markets – as provider of natural resources – and bringing certain levels of economic growth and development. Nevertheless, this is not experienced equally by most of the population who see their natural environment depleted and receive little benefit from this ‘development’.

These complexities and the emerging inequalities pose the challenge of coordinating political efforts to revert the situation and implement policies and strategies to promote human rights, environmental restoration, and sustainable development.

Uganda finds inspiration in international, regional and national standards and instruments to promote peace, environmental protection and human rights. There is, for instance, a resolution by the African Commission from 2012 calling for a Human Rights-Based Approach to Natural Resources Governance (21) urging member states among other issues to “[e]nsure that respect for human rights in all matters of natural resources exploration, extraction, toxic waste management, development, management and governance, in international cooperation, investment agreements and trade regulation prevails”.

The country – it is claimed – has made progress in domesticating human rights standards and incorporating environmental concerns in its legislative frameworks.  The Constitution of Uganda in article 39 provides that every citizen has the right to a clean and healthy environment; and since 2019, the Ugandans have a national law to protect the natural environment and regulate how it should be used: the National Environment Act. In fact, there are many acts, policies and plans at the central level dealing with the promotion of sustainable use of the natural environment and nature protection, such as those dealing with biodiversity, wildlife, forestry, tree planting, water, wetlands or land.

Local and central authorities also play a key role in the protection of human rights and the environment, with the creation of bills and policies, such as the drafting of the Acholi Sustainable Charcoal Production and Marketing Bill from 2019 (22).

In this context, I argue that the ‘problem’ is not the lack of environmental or human rights recognition or legislative frameworks, but the way these are implemented (or silenced). I am referring not only to environmental interventions, but also to human rights ones.

Human rights interventions I have in mind are those that go hand in hand with environmental protection and ecological restoration. The natural environment cannot be left aside in planning, designing, implementing, monitoring, or evaluating human rights strategies. Such strategies should work towards political empowerment, sustainable development, and peace for all, and particularly for those more in need. They should be attentive of not (re)producing conflicts.

Branch (2011: 9) points out that “human rights intervention may inadvertently provide the tools for emancipatory politics, politics possibly based upon concepts of human rights that imply and depend on individual and collective social and political agency” (23).  I believe that the role of journalists and civil society in denouncing environmental injustices and/or human rights violations are central in promoting a real implementation, monitoring and evaluation of the existing international and national laws and policies. Members of diverse organisations of the civil society with support from (and despite of) the international community are nowadays active in denouncing the ongoing environmental deterioration (24) and human rights abuses in Uganda.

The question remains then for the different authorities in Uganda and for Ugandan peoples to collectively discuss and decide how they wish the Northern region to be integrated to the rest of the country and the global economy, how to promote alternative sources of energy, and how to restore degraded natural environments, while promoting, protecting and fulfilling human rights for all.

 

Acknowledgments

I would like to thank Patrick Okullo for his time to chat and enlighten me about his work and worries from those living in Acholi and other sub-regions in the North of Uganda. I extend my gratitude to my colleagues Kasiva Mulli, Yvonne Oyieke and Alice Kasznar for their feedback to draft versions of this blog-post.

Notes

[*] Lira is a town in Lango sub-region, which has also been affected by the armed conflict as IDP camps were located there.

 

References

(1) HRC (2007) “Report on the work of the Office of the High Commissioner for Human Rights in Uganda”, Report of the High Commissioner for Human Rights and follow-up to the World Conference on Human Rights Addendum. Human Rights Council. A/HRC/4/49/Add.2. Available online here.

(2) OHCHR (2013) “Report on the Activities of the Office of the United Nations High Commissioner for Human Rights and the Human Rights Situation in Uganda”, Nov. 2011 to Sept. 2013. Available online here.

(3) HRC (2016) National report submitted in accordance with paragraph 5 of the annex to Human Rights Council resolution 16/21. Uganda. Working Group on the Universal Periodic Review Human Rights Council. Available online here.

(4) UN (2004) “Specific groups and individuals. Mass exoduses and displaced persons”, Report of the Representative of the Secretary-General on internally displaced persons, Deng, Francis. Mission to Uganda. Economic and Social Council, United Nations. Commission on Human Rights. E/CN.4/2004/77/Add.1. Available online here.

(5) Oroma, Gladys (2008) “The forgotten ‘victim’ of the northern Uganda war”, news article in Daily Monitor Only (Uganda) June 4. Available online here.

(6) Nampindo, Simon; Picton-Phillipps, Guy & Plumptre, Andrew (2005) The impact of conflict in Northern Uganda on the environment and natural resource management, USAID and Wildlife Conservation Society. Available online here.

(7) TNH (2012a) “Charcoal boom a bust for forests”, news article in The New Humanitarian (formerly IRIN News). 7 February. Available online here.

(8) Ministry of Water and Environment (2016) “State of Uganda’s Forestry”. The Republic of Uganda. Available online here.

(9) Owiny, Tobbias Jolly (2020) “LRA war victims beat odds to succeed in dairy farming”, news article in Daily Monitor. 18 August. Available online here.

(10) Branch, Adam & Martiniello, Giuliano (2018) “Charcoal Power: The Political Violence of Non-Fossil Fuel in Uganda”, in Geoforum, 97: 242-252. Online here.

(11) TNH (2012b) “Land disputes threaten northern peace”, news article in The New Humanitarian (formerly IRIN News). 19 April. Available online here.

(12) Otim, Denis Barnabas (2012a) “Uganda: Local land dispute threatens violence”, blogpost in Peace Insight. 27 December. Available online here.

(13) Otim, Denis Barnabas (2012b) Is it oil, land or investment triggering increasing land dispute in Lakang village of Amuru district? Situation report. Refugee Law Project, School of Law, Makerere University and Advisory Consortium on Conflict Senstivitiy (ACCS). Available online here.

(14) Otim, Denis Barnabas (2012c) “Dealing with land conflicts in Amuru, Uganda”, blogpost in Peace Insight. 13 Noviembre. Available online here.

(15) Otim, Denis Barnabas (2013) “Uganda: Investors must involve the locals in acquiring land for investment”, blogpost in Peace Insight. 04 March. Available online here.

(16) Taylor, Liam (2019b) “’This is our land’: Uncertain future for Ugandans facing eviction from wildlife reserve”, news article in Thomson Reuters Foundation. 23 July. Available online here

(17) Kitara, Jackson (2018) “Environment committees to fight charcoal burning”, news article in New Vision. 20 July. Available online here.

(18) Muhumuz, Rodney (2019) “Africa’s charcoal trade is decimating fragile forest cover”, news article in The Associated Press (AP). September 25. Available online here.

(19) Owiny, Tobbias Jolly (2019) “Why illegal logging, charcoal burning persists in the north”, news article in Daily Monitor. 3 November. Previously available online here.

(20) Doom, Ruddy & Vlassenroot, Koen (1999) “Kony’s Message: A New Koine? The Lord’s Resistance Army in Northern Uganda”, in African Affairs 98 (390): 5-36. Available online here.

(21) ACHPR (2012) Resolution on a Human Rights-Based Approach to Natural Resources Governance, African Commission on Human and Peoples’ Rights. Available online here.

(22) Labeja, Peter (2019) “Acholi Region Drafts Charcoal Policy”, news article in Uganda Radio Net (URN). 20 February. Available online here.

(23) Brach, Adam (2011) Displacing Human Rights: War and Intervention in Northern Uganda. Oxford University Press, Oxford. Available online here.

(24) Taylor, Liam (2019a) “’Cutting everything in sight’: Ugandans vow to curb rampant deforestation”, news article in Thomson Reuters Foundation. 12 March. Available online here.

October 16, 2020

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Colombia’s environment in the post-conflict transition – New set-backs by the global pandemic

Farm landscape in the Putumayo department, Colombia. Photo taken by Torsten Krause, December 2019

By Torsten Krause*, Ana Maria Vargas Falla**, Britta Sjöstedt*, Sandra Valencia***, Fariborz Zelli*[1]

A glimpse of hope quickly vanishing

In 2016, Colombia officially emerged from one of the world’s longest internal armed conflicts when the government, under former President Juan Manual Santos, signed a peace agreement with the country’s largest and most influential guerrilla group, the Revolutionary Armed Forces of Colombia – People’s Army, also known as FARC.

Four years have passed since, and while some of Colombia’s departments have been able to enjoy a relatively tranquil time with the retraction of the FARC and the cessation of hostilities and violence, other departments and rural areas, have moved even further away from peace. For decades the FARC had exercised a de-facto state authority with rules and regulation in the territories previously under its control. However, since October 2016, when the FARC retracted from these territories as part of the demobilization process, the void has often been filled by a diverse range of new armed groups including criminal gangs. These gangs, referred to by local authorities as BACRIM,[2] have been trying to seize control of lucrative informal markets including the coca and gold trades. In addition, the power vacuum was filled by other leftist guerilla groups that have been fighting the Colombian state for decades. These include, foremost, the National Liberation Army (ELN)[3], but also former FARC guerilla fighters who rejected or abandoned the re-integration process and formed FARC dissident groups.

Thus far, the outcome of these developments is a complex mixture of violent armed groups, all of which profit financially from the general chaos of the power vacuum. While some of them, such as the ELN, claim to pursue larger political objectives, what all of these groups have in common is their main modus operandi, that implies a dangerous cocktail of illegal practices, violence and intimidation of local populations, including peasants, social leaders, international and local non-governmental organizations (NGOs) as well as large multinational corporations.

Farm run by former FARC guerilla members, Municipality of Puerto Guzmán, Putumayo department, December 2019. Photo taken by Torsten Krause

The consequences reverberate through rural Colombia once again in the form of forced displacements of thousands of families in the departments of Antioquia, Caquetá, Cauca, Chocó, Nariño, Norte de Santander, Putumayo, and Santander. Hundreds of civilians have been murdered, including numerous social and indigenous leaders that had demanded access to land and resources, had defended the rights of indigenous peoples, had tried to defend communities from illegal mining and drug trade, had been involved in coca eradication initiatives, or had protected the environment from polluting mining practices and illegal logging[4]. This continuous conflict has earned Colombia the inglorious 2nd and 3rd places, respectively, among the countries with the highest number of assassinations of human right defenders and social and environmental leaders in the past four years (Witness 2017, 2019, UN 2020).

A new victim: The environment

Thus, while it might seem from an outsider’s perspective that the Colombian armed conflict has come to an end, the life of many people in rural areas is in reality marked by ruthless violence and intimidations that have come to haunt areas of the countryside once more. What is new this time is that the targets of harm include not just human beings, such as farmers, social leaders and indigenous people, but also the natural environment. Ever since the cease fire between the FARC and Colombian state in 2014 and the signing of the peace agreement in 2016, deforestation in Colombia has soared and there is a strong overlap between areas that record high levels of violence since the peace agreement and those that exhibit illegal conversion of forests to agricultural land uses, cattle pastures and coca plantations (Prem et al. 2018, Negret et al. 2019, Clerici et al. 2020, Murillo Sandoval et al. 2020). In particular the Amazon frontier departments of Colombia are experiencing a sharp rise in deforestation (see Fig.1) (Clerici et al. 2020).

Deforestation rates in Colombia, the Amazon region and individual Amazonian departments. The dashed line in 2014 indicates the year when the indefinite ceasefire between the FARC and the Colombian government was agreed. Source: Global Forest Watch 2020.

To make matters worse and more complicated, environmental and social organizations are becoming a target of intimidation and violence too. A recent pamphlet that was circulated, supposedly by a FARC dissident group, sends a warning to anybody who collaborates with organizations working on environmental projects in the Amazons and other regions. The pamphlet explicitly mentions international organizations (namely, the Organization of American States – OAS and USAID), national programs to fight deforestation (Visión Amazonía), research institutions (the Colombian Institute for Amazonic Scientific Research – SINCHI), regional environmental authorities (in particular, the Corporation for the Sustainable Development of the North and Oriental Amazon – CDA; and Corpoamazonia) as well as the Colombian National Park Authority (Infoamazonia, April 16, 2020).[5] In the past months, national park rangers have been increasingly targeted by armed groups, some have been assassinated, and they had to abandon their posts in many of the national parks in the Andean-Amazon region, unable to control intrusion and deforestation.

In recent months alone, deforestation has considerably soared again, and is particularly severe in the Tinigua and La Macarena national parks in the Meta department, as well as in the Nukak indigenous reservation in the Guaviare department (FIP, 2020).[6] There are several explanations for this development, but it is first and foremost attributable to processes of land grabbing, mainly by large landowners, who seek to use the current void and absence of state control to expand their land holdings by cutting down large stretches of forests (Van Dexter and Visseren-Hamakers 2019, Murillo Sandoval et al. 2020). By putting cattle on these newly deforested areas they hope to be able to claim these lands in the future. Put differently, the peace agreement and FARC’s demobilization raise expectations and opportunities of big land owners to eventually obtain legal land titles. Unfortunately, thus, the peace process must be considered an unintended driver of land grabbing and illegal land markets (Murillo Sandoval et al. 2020).

Apart from the serious long-term environmental consequences that deforestation leads to, it also brings to light the underlying issue that fueled the armed conflict in Colombia in the first place, namely the highly unequal access to, and control of, land in Colombia. A small share of landowners possesses the majority of agricultural lands in the country. This unequal distribution was, ironically, perpetuated by armed groups during the conflict due to the violent displacements of small-scale farmers, and it has now further increased in the aftermath of the peace agreement (Guereña 2017).

Recent patches of deforestation in the Guaviare department. Photo taken by Torsten Krause, June 2017.
The Amazon frontier region in the Guaviare department with encroaching agricultural activities. Photo taken by Torsten Krause, June 2017.

The rise in coca plantations over the past 10 years is another environmentally harmful development that complicates Colombia’s transition to peace (Fig. 2). During the armed conflict the production and trade of cocaine was a major income generating activity for different factions. The FARC, ELN and paramilitaries used it to finance their operations, buy weapons, pay their soldiers and make a lot of money. The high profitability of the globally demanded product, the established system from cultivation, production to export as well as the acquired know-how in Colombia, all facilitate the continuation of the lucrative cocaine trade. The current trade includes some of the actors from before the peace agreement, but also new ones that seek to control the business, most notably notorious Mexican cartels, such as the Gulf, Sinaloa and New Jalisco cartels.

Furthermore, Colombia has also experienced an increase in the mining of minerals, such as gold and coltan (Ballvé 2012, Guevara et al. 2016). By some estimates, approximately 85% of precious ore mining in Colombia, in its majority gold, is illegal.[7] Armed groups are often involved in these mining and trade operations. The use of mercury in the extraction process is resulting in devastating health and environmental consequences for local populations, rivers and forests. A rise in homicides and massacres associated with illegal gold mining has also been reported (Guevara et al. 2016).

Extent of coca cultivation in Colombia. Source: U.S. Office of National Drug Control Policy (ONDCP)

A new set-back by Covid-19

The aforementioned setbacks to the post-conflict transition, and the negative social and environmental impacts in particular, are further exacerbated and reinforced by the Covid-19 pandemic caused by the current coronavirus (SARS-CoV-2). In addition to its detrimental health impacts, the Covid-19 pandemic has developed into a powerful social and political force by occupying and channeling key public discourses and political attention. With these multi-dimensional implications, we argue that the current pandemic poses a major threat for the Colombian peace transition and for the natural environment in several ways.

First, the crisis caused by the spread of the coronavirus and the ensuing strict stay-at-home quarantine, declared nation-wide by President Duque from March 24 this year, has diverted considerable attention and response capacities away from the tensions in rural and frontier areas (FIP, 2020, p. 16). This reinforces the already existing governance gaps in these areas at a time when both local vulnerable communities and the environment are in even higher demand of protection.

With regard to vulnerable groups, the violence in Colombia’s rural areas has continued despite the quarantine, and there have been numerous registers of assassinations of social and indigenous leaders during the lockdown.[8] The Ideas for Peace Foundation (FIP – Fundación Ideas para la Paz in Spanish) argues that social and indigenous leaders can be more vulnerable during the quarantine as their routines and locations become more predictable. In its recent report on armed conflict dynamics during the pandemic FIP provided evidence showing that attacks on oil pipelines have intensified over the first four months of 2020, while deforestation and illegal mining practices are persisting.

These worrying developments notwithstanding, there are a few signs of improvement. For one, the overall number of attacks carried out by armed groups has declined in April. This may be explained by the ELN’s declaration of cease fire with a view to the corona crisis (FIP, 2020, p. 8).  Likewise, the number of violent deaths has been steadily decreasing since early 2019 in municipalities that are implementing specific initiatives based on the peace agreement. These include the Development Programs with Territorial Focus (PDET in Spanish) and the National Program for the Integral Substitution of Illicit Crops (PNIS in Spanish) (ibid., p. 13). Nonetheless, a few areas have not followed this positive trend though and instead witnessed and increase in the death toll. This goes for Santa Marta in the Magdalena department, Tarazá and Segovia in Antioquia, and most notably in El Tambo in Cauca (22 violent deaths between January and April 2020, compared to 8 during the same period in 2019) (ibid., p. 15).

With respect to the environment, armed groups, settlers (colonos) and landgrabbers have been further moving into forested areas, causing massive deforestation during the coronavirus crisis, while environmental organizations, both public and private ones, can do even less due to the quarantine-related mobility restrictions (FIP, 2020). The example of Brazil gives a bleak outlook of what more is about to happen in Colombian Amazon regions. In Colombia’s biggest neighbor, deforestation in the Amazon region has soared considerably in the first weeks of the Covid-19 pandemic, also due to the reduced enforcement power of the national environmental agencies.

In addition to these direct social and ecological consequences of pandemic, we expect stark indirect negative impacts, fueled by global economic downturn. The associated fall in demand for oil has already resulted in a slump of oil prices, which, in turn, has entailed a substantial increase of the price for gold. This provides an incentive to further expand gold mining activities and will likely exacerbate violence and its severe negative social and environmental repercussions (Guevara et al. 2016, Rodríguez and Galvis 2016).

As one example of such a dynamic, the Wiwa indigenous group, located in the Guajira department in the north of the country, reported that, during the pandemic, illegal mining of gold in their ancestral territory has intensified. Studies conducted in the area prior to the pandemic had already revealed high concentrations of heavy metals in rivers and fish attributable to mining activities.[9] These activities are carried out by outsiders who carry weapons and are often linked to armed groups. Besides the immediate concerns for security and environment,[10] the Wiwa community is worried about a heightened risk of SARS-Cov2-infection by the illegal miners (FIP, 2020).

A challenging road ahead

Colombia’s transition to peace is heading towards a difficult path and the Covid-19 pandemic is most likely more than a minor roadblock. Due its major social and environmental consequences, it may undermine the small positive efforts taken towards a sustainable peace so far.

Where does this lead us? On the one hand, and in spite of these developments and dynamics, many people in Colombia do still believe in the peace process. The FARC party, composed of demobilized leaders, frequently reinstates its commitment to the process. Efforts continue to integrate FARC ex-combatants into civilian life. Some of these efforts include agricultural projects, training programs and conservation initiatives (e.g. Ambientes para la Paz – Environments for Peace program[11]). In addition, even if peace talks have not succeeded with the ELN, some of its members are starting to demobilize[12].

On the other hand, the Colombian government struggles to build lasting and sustainable peace. Already before the current pandemic, the government had been in a balancing act. It had to keep up its discourse to build lasting peace and to satisfy the demands of international forest conservation activists and project donors (Krause, 2020). On the other hand, pressure has been mounting from within the government and the private sector to gear up the extraction of natural resources in the form of mining, infrastructure and industrial agriculture (DNP 2018). Such activities, however, are more akin to traditional models of economic growth.

There is no doubt that Colombia’s social and environmental problems are considerably shaped by global market demands for agricultural produce, oil, minerals and coca. This notwithstanding, there are fundamental domestic reasons, starting with governmental policies that directly and indirectly incentivize environmental degradation. The strong inequalities in land access and ownership that have been underlying the decade-long armed conflict have still not been tackled sufficiently. Instead, the severe enforcement gaps to address land grabbing and illegal mining de facto turn a blind eye to local corruption, violence and assassinations. As long as these contradictions and shortcomings are not openly discussed and acted upon in a comprehensive manner, the armed conflict over resources and land will be perpetuated – and with it the severe social and environmental crisis in Colombia.

References

Ballvé, T. 2012. Everyday State Formation: Territory, Decentralization, and the Narco Landgrab in Colombia. Environment and Planning D: Society and Space 30:603-622.

Clerici, N., D. Armenteras, P. Kareiva, R. Botero, J. P. Ramírez-Delgado, G. Forero-Medina, J. Ochoa, C. Pedraza, L. Schneider, C. Lora, C. Gómez, M. Linares, C. Hirashiki, and D. Biggs. 2020. Deforestation in Colombian protected areas increased during post-conflict periods. Scientific Reports 10:4971.

DNP. 2018. Bases del Plan Nacional de Desarollo 2018-2022. Page 945 in D. N. d. Planeación, editor. Government of Colombia, Bogotá.

FIP. 2020. Dinámicas de la Confrontación Armada y su Impacto Humanitario y Ambiental: Tendencias en la Pandemia – Enero a Abril 2020. Fundación Ideas para la Paz, Bogotá.

Guereña, A. 2017. A Snapshot of Inequality – What the Latest Agricultural Census Reveals About Land Distribution in Colombia. Oxfam.

Guevara, E. L., N. Duarte, and E. Salcedo-Albarán. 2016. Introduction to Trafficking of Gold and Coltan in Colombia. Vortex Foundation, Bogotá.

Krause, T., Reducing deforestation in Colombia while building peace and pursuing business as usual extractivism? Journal of Political Ecology, 2020. 27(1): p. 17.

Murillo Sandoval, P. J., K. Van Dexter, J. Van Den Hoek, D. Wrathall, and R. Kennedy, E. . 2020. The end of gunpoint conservation: Forest disturbance after the Colombian peace agreement. Environmental Research Letters.

Negret, P. J., L. Sonter, J. E. M. Watson, H. P. Possingham, K. R. Jones, C. Suarez, J. M. Ochoa-Quintero, and M. Maron. 2019. Emerging evidence that armed conflict and coca cultivation influence deforestation patterns. Biological Conservation:108176.

Prem, M., S. Saavedra, and J. F. Vargas. 2018. End-Of-Conflict Deforestation: Evidence from Colombia’s Peace Agreement. Universidad de Rosario, Bogotá.

Rodríguez, C. A., and S. R. Galvis. 2016. El oro, la contaminación y los seres del agua. Visiones locales de los impactos ambientales de la minería en el mundo acuático de la Amazonia colombiana., Tropenbos Internacional Colombia.

UN. 2020. Colombia: ‘Staggering number’ of human rights defenders killed in 2019. United Nations, n/a.

Van Dexter, K., and I. Visseren-Hamakers. 2019. Forests in the time of peace. Journal of Land Use Science:1-16.

Witness, G. 2017. Environmental Activists. Global Witness, London.

Witness, G. 2019. Enemies of the state? How governments and business silence land and environmental defenders.


[1] Affiliation: *Lund University, ** Swedish International Centre for Local Democracy, *** Chalmers University of Technology.

[2] In its nomenclature of 2016, the Ministry of Defense (through the Directiva permanente 15 de 2016)officially distinguished Criminal Bands (Bandas Criminales – BACRIM) from Organized Armed Groups (Grupos Armados Organizados – GAO)and Organized Crime Groups (Grupo Delictivo Organizado GDO).

[3] There have been several attempts to hold peace negotiations between the Colombian Government and the ELN. In October 2016, both parties announced the initiation of peace talks, which officially started in February 2017 in Quito, Ecuador. However, the talks faced several obstacles including the ELN refusing to release kidnapped hostages. The negotiations were cancelled by President Ivan Duque after ELN attacked a military school in Bogotá killing 21 people and injuring 68 in January 2019.

[4] According to January 2020 data from the Colombia Ombudsman Office, an estimate of 555 social leaders were assassinated since 2016 (https://www.defensoria.gov.co/es/nube/enlosmedios/8996/Al-menos-555-l%C3%ADderes-sociales-han-sido-asesinados-entre-2016-y-2019-Defensor%C3%ADa-del-Pueblo.htm).

[5] See: https://www.elespectador.com/noticias/medio-ambiente/panfletos-firmados-por-disidencias-de-las-farc-invitan-deforestar-la-amazonia-articulo-914948

[6] See: https://www.eltiempo.com/vida/medio-ambiente/la-deforestacion-va-a-un-ritmo-exagerado-con-o-sin-pandemia-488750

[7] See: https://www.eltiempo.com/vida/medio-ambiente/coronavirus-en-colombia-francia-marquez-explica-por-que-mineria-se-incrementara-tras-la-pandemia-490444

[8] See: https://www.elespectador.com/colombia2020/pais/los-rostros-y-luchas-de-los-lideres-sociales-asesinados-en-lo-corrido-del-2020-articulo-913792

[9] https://sostenibilidad.semana.com/medio-ambiente/articulo/la-mineria-ilegal-azota-al-territorio-wiwa/47864

[10] https://www.eltiempo.com/vida/medio-ambiente/en-cuarentena-indigenas-denuncian-mineria-ilegal-en-su-territorio-490582

[11] https://www.co.undp.org/content/colombia/es/home/projects/ambientes-para-la-paz.html

[12] https://www.semana.com/nacion/articulo/colombia-no-puede-tener-la-pandemia-del-virus-y-la-pandemia-de-la-violencia/667189

May 31, 2020

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Colombia environmental peacebuilding

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New research project: At the nexus between peace and nature in Uganda and Colombia

We will evaluate the changes in livelihoods and their impacts on the natural enviroment after the end of the armed conflict.Credit: Brian Harries, licensed under CC BY 2.0

From the Amazon forest and the Andean mountains in Colombia to the vast plains and valleys in northern Uganda, The Nature of Peace research group will explore the connection between the peace processes and the ongoing environmental changes and their social and human rights implications in these two post-conflict societies.

For the next three years, our interdisciplinary research team – with members from Lund University, the Raoul Wallenberg Institute of Human Rights and the University of Gothenburg –  will investigate how peace peacebuilding impacts the natural environment and how, in turn, environmental concerns are integrated into stabilization policies of these two countries.

The cases of Colombia and Uganda bring key insights about the connections between the natural environment and the post-conflict policies. Credit: Laura Betancur A. and Nina R. licensed under CC BY 2.0

Both cases bring relevant insight into the environmental peacebuilding research agenda. On the one hand, Colombia and Uganda have similar trends regarding low environmental awareness and dominance of resource-exploiting preferences and discourses. On the other hand, they provide geographical diversity with their embeddedness in two world regions, Latin America and Sub-Saharan Africa, respectively. Additionally, we expect novel and timely insights considering the recent post-conflict phase in Colombia since 2016; and more longstanding outcomes from the peace processes in Uganda, where the stabilization period has taken place since 2007. 

For both countries, we mainly inquire to which extent there are concerns of environmental protection integrated or neglected in the post-conflict peacebuilding process? To gain a deeper understanding, we aim to identify the major drivers and conditions underlying this integration or neglection.

Consequently, we will also investigate the impacts of these considerations on the natural environment, livelihoods of local communities, vulnerable groups and on political conditions that also influence peace itself. With this knowledge, we expect to compile helpful lessons for societies that have similar situations in the present or the future.

Initially, we have selected specific protected areas and their buffer zones for our fieldwork in Colombia and Uganda. In 2020, four researchers (two scholars per country) will conduct interviews and focus groups with key social groups and institutions, narrative and transect walks in different areas, and workshops with community members.  

We expect novel and timely insights considering the recent post-conflict phase in Colombia since 2016; and more longstanding outcomes from the peace processes in Uganda.

The Nature of Peace Project

Along with fieldwork, we will develop a spatial analysis to understand land-use changes in the areas under studied; and will also conduct legal and policy analyses. During these years, we will collaborate with researchers, universities and international cooperation agencies in Colombia and Uganda.

The photo shows deforested areas in the Colombian Amazon. Since the signing of the peace agreement, the deforestation rate has doubled in the country. We will analyze these changes in land-use changes in our research. Credit: Ideam, Colombia.

With this exciting research journey, we expect to provide comprehensive theoretical frameworks and systematic comparative empirical analyses for the intersection between post-conflict peacebuilding and the environment and the communities depending on it.

At the same time, we seek to contribute to prevent further negative consequences for the natural environment and current and future generations once protracted violent conflicts come to an end.

Our research team

Researchers

Fariborz Zelli (Project leader)
fariborz.Zelli@svet.lu.se

Sandra Valencia (Colombia case)
sandra.valencia@chalmers.se

Torsten Krause (Colombia case)
Torsten.Krause@lucsus.lu.se

Maria Andrea Nardi (Uganda case)
maria.andrea.Nardi@rwi.lu.se

Joshka Wessels (Adviser)
joshka.wessels@cme.lu.se

Britta Sjöstedt (Law and policy analysis/Colombia case)
britta.sjostedt@jur.lu.se

Micael Runnström (GIS Analysis/Uganda case)
micael.runnstrom@nateko.lu.se

Alejandro Fuentes (Law and policy analysis)
alejandro.fuentes@rwi.lu.se

Research assistants

Laura Betancur (2019-2020)
Alice Kasznar Feghali (2019-2020)

November 25, 2019

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Colombia environmental peacebuilding

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Three provocative ideas in the first Environmental Peacebuilding Conference

Gold miners
Screenshot from the photo essay by Nancy Lee Peluso about gold miners in Indonesia. Peluso participated from the Environmental Peacebuilding Conference at Irvine, California.

Under the umbrella of “environmental peacebuilding”, a growing community of researchers and practitioners are framing their efforts in relating the natural environment and the peacebuilding agenda in several countries around the world. As I described in a previous post, last week, this community got together in the First Environmental Peacebuilding Conference in Irvine, California (US). Among all the presentations and case studies, three outstanding interventions called my attention to reflect on my own research work. Here, I want to share interesting insights to look ahead in the field: 

The three researchers called the attention for critical views in the field of Environmental Peacebuilding.From left to right: Elaine (Lan Yin) Hsiao, Teresa Lappe-Osthege, and Nancy Lee Peluso..

Looking backward to understand the future. During the second session on Thursday (October 24) about ‘Early Linkages in Environment, Conflict, and Peace’, someone in the audience asked about the future of research in the environmental peacebuilding field. Far from typical answers on technology applications or climate change scenarios, Elaine (Lan Yin) Hsiao, a Global Challenges Fellow at the Sheffield Institute for International Development (SIID), claimed that one need of the field is to ‘look backward’ to understand colonial tensions and those are embedded in the socio-ecological conflicts. Her mention of the colonial aspect shed light on the “elephant” in the room and made me reflect: How much are we addressing colonial and post-colonial influences in the analysis we do on our cases? How, in the development practices, are we solving previous colonialist sources of conflict to promote a better balance between conservation and social justice?

Contesting our views on “peace” and “conflict” dynamics in the territories. On Friday, the political ecology professor Nancy Lee Peluso, from the University of California Berkley, gave an interesting presentation on ‘Landscapes of violence and peace’ with focus on her work in small-scale gold mining in Indonesia. Peluso presented how miners viewed their activity as a ‘peaceful moment’ in contrast to other perspectives emphasizing the violence in the same transformed territories. She called attention to understand how some “types” of violence are more accepted than others, for instance, the political violence affecting this region. Likewise, she invited the audience to focus on labor transformations to understand the political economy of the territories and the roots of conflicts.  Peluso opened a valuable discussion to revise our pre-fixed normative conceptualizations on peace and conflict and how value judgments can prevent us from a more comprehensive view of the local territorial dynamics.

During her presentation, Peluso shared her photo essay about the lives of ‘gold farmers’ in Indonesia.

Is environmental peacebuilding covering up neoliberal approaches? On Thursday (October 24), Teresa Lappe-Osthege, research associate on the Biosec project, made a very interesting presentation about how the concept of environmental peacebuilding can be used to cover up neoliberal peace approaches. Her presentation, focusing on EU peacebuilding policies in Kosovo, showed that perspectives on sustainability remained stagnant in views about security and development, without addressing existing socio-ecological injustices in the country. Teresa highlighted the relevance of a more critical reflection on the practices and narratives we are allowing to be framed under the umbrella of environmental peacebuilding.

November 25, 2019

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