Introduction
At the core of Africa’s decolonisation perspective on the Anthropocene lie longstanding and ongoing histories of colonial and capitalist modernity that have shaped and continue to shape vulnerabilities of the continent to changes in ecosystems and natural environments (
van Klinken et al. 2024). Whilst literature on environmental politics reveals ongoing processes of enclosure, commodification and dispossession of African resources under the guise of climate change mitigation and adaptation (
Manda & Nyambe 2023),
van Klinken et al. (2024) have argued that indigenous and local knowledge (ILK) remains important not only for understanding traditional responses to environmental changes but also for how these could be framed for uptake in climate action—an important epistemological feature. By acknowledging ‘the value of diverse forms of knowledge such as scientific, as well as Indigenous knowledge and local knowledge in understanding and evaluating climate adaptation processes and actions to reduce risks from human-induced climate change’ (
IPCC 2022: 7), the Intergovernmental Panel on Climate Change (IPCC) opened new intellectual ground requiring empirical examination of the state of play of ILK and the implications for adaptation. Scholars in African environmental studies have engaged diverse disciplinary perspectives and methodologies in humanities (
Oba 2014), literary and cultural studies (
Aghoghovwia & McGiffin 2024), philosophy (
Chemhuru 2022) and religion (
van Klinken 2021). Doing so, they have begun to unravel the social and cultural epistemologies through which local communities understand vulnerability and respond to climate change and how this knowledge could go to the heart of policy and action. Indeed, to many indigenous communities, climate change is not a new feature, and recent evidence demonstrates how ILK helps to strengthen the understanding of human–environment relationships, increasing the effectiveness, sustainability and equity of adaptation measures (
Carmona et al. 2023: 1). Advancing African ecologies, van Klinken
et al. (
2024: 2) have invited us to be creative and innovative in the quest to understand, address and possibly fund solutions for the major environmental challenges on the continent. Whereas development actors internationally and nationally have responded through initiatives that incorporate local communities as architects of adaptation strategies, the application of ILK in climate adaptation strategies remains an interesting area of research—and is a focus of this study.
Climate adaptation is framed loosely as change—for example, behaviour, social or economic—meant to reduce risk in response to, or in anticipation of, climate change (
Pisor et al. 2022). International development actors such as the World Bank are acknowledging and integrating local communities as part of community driven climate adaptation (CDCA) strategies (
Kandel et al. 2023). Yet, ILK remains peripheral to mainstream climate science and adaptation initiatives, which typically uphold and privilege Western science and ‘experts’ within the hierarchy of scientific evidence—often resulting in the top-down implementation of contextually inappropriate and ineffective policy solutions that risk exacerbating existing inequities and marginalisation (
Milbank et al. 2021). Specifically, a general focus on the science of the climate crisis and ecological collapse, and related marshalling of technocratic knowledge about climate in the literature has failed in terms of mass appeal or providing clear material benefits for poor ‘communities’ (frequently framed as rural, indigenous and/or poor in adaptation projects) (
Huber 2022).
Various actors have emphasised the need to reframe and advance adaptation in line with lived experiences, capacities and aspirations of self-determination. These calls have gained credence in the scholarship on decolonising climate and adaptation (
Johnson et al. 2022). There are repeated calls for ‘communities’ on the frontline of climate change to take the lead in choosing their own adaptation (
Pisor et al. 2022). As with other investment projects, supporting ‘community’ autonomy is seen as an important component for sustainability and equity (
Manda 2022), and that the effectiveness of climate change adaptation depends on this (
Pisor et al. 2022). The argument is that co-optation of ‘community’ in climate adaptation aligns solutions to local conditions, needs, values and norms, leading to sustainable risk reduction. How ILK is framed and integrated in adaptation projects is less understood.
This article reflects on four important dimensions of climate adaptation intervention:
1.
the local framings and understanding of vulnerability and climate change response pathways from a social and cultural perspective;
2.
the structure and organisation of CDCA measures and the integration of local climate needs;
3.
the integration or marginality of ILK in CDCA projects and implications thereof;
4.
how ILK could be deployed to help build climate resilience and expand inventories of adaptation possibilities for communities supposed to be adapting.
The rest of the article is organised as follows. The next section (2) presents methods. Section 3 focuses on how local communities in rural Zambia experience government–donor CDCA initiatives across the 4 dimensions and is followed by a discussion section (4), which situates the former into the wider empirical and theoretical context. The concluding sections reflect on (5) the study results, particularly the marginality of ILK, and (6) how CDCA initiatives can be structured and organised to expand inventories of possibilities for adapting communities and to shape the sustainability and equity of adaptation measures.
Using donor CDCA projects to analyse ILK
Using donor-driven CDCA as an avenue for analysing the integration (or marginality) of ILK in climate adaption allows for an exploration of how powerful development actors engage with ILK. Recent efforts aimed at the decolonisation of knowledge can only be effective if donor efforts are unpacked.
The Barotse floodplain—also known as the Bulozi plain or Zambezi floodplain—is one of the greatest wetlands in Africa.
1 It is inhabited by the Lozi-speaking people and is found in the western region of Zambia (about 600 km from the capital Lusaka). The floodplain is 230 km long with a width between 30 and 50 km, with peak water levels in the months April to July, and the month of November being the period when the water levels are the lowest (
Sampa et al. 2019). The timing and duration of annual floods determine the conditions of the plain and the way it supports production and livelihoods. Subsistence agriculture dominates, drawing about 280,000 ha of land into herding, cropping (for example, rice, maize, cassava, sorghum and millet) and fishing, livestock and natural resources. The region is one of the most vulnerable regions to climate change, attracting policy attention (
Funder & Dupuy 2022).
In Zambia, the Strengthening Climate Resilience in the Barotse Sub-basin (SCReBS) project has since 2013 been implemented under the Pilot Programme for Climate Resilience (PPCR) through the Ministry of Green Economy and Environment (MGEE) and funded by Climate Investment Funds. Phase 1 of the PPCR (2010–13) focused on mainstreaming, capacity building and information sharing at the national level. The project was extended to Phase II (2014–19) and, with additional financing from the World Bank of US$14.6 million, to 2022 (
Sinyangwe 2020). The project aimed to strengthen climate resilience through the development of livelihoods and infrastructure. Each participating local group opened a bank account allowing direct transfers of funds. Each sub-project has a management committee: a chairperson, treasurer, secretary and at least three committee members. Sub-grants have funded diverse sub-projects (
Appendix), with participating communities receiving between ZMW40,000 and ZMK250,000.
2 Community in this project is constituted as the local groups identified/selected to manage adaptation grants and sub-grants. We purposively selected SCReBS based on its focus on climate-risky areas in Zambia and its focus on drought and flood risk resilience. Communities in the Barotse sub-basin are among the poorest (
Milupi et al. 2020) and most vulnerable to climate change, while at the same time they lack resources to adapt to significant changes in their local ecosystems (
MNDP 2015). However, the Lozi speaking people have rich ecological knowledge, adapting for decades to flood disasters. The SCReBS project supports
ex ante risk climate and disaster risk reduction in the disaster-prone Barotse sub-basin, improving livelihoods and strengthening resilience to climate variability.
We selected participants of climate adaptation sub-projects, including project staff (at provincial and district government levels) to solicit views on the CDCA and related outcomes. In selecting participants, we considered gender and age, and where possible longevity in the project, including case studies of local knowledge holders. We selected four districts (Nkeyema, Kaoma, Luampa and Mongu) in the northern part of the Barotse Sub-Basin and three (Sioma, Mwandi and Kazungula) in the southern part.
There are about 1,650 sub-projects in the Barotse Sub-Basin. We selected 20 sub-projects under three broad project formulations: hard, soft and integrated strategies. Small-scale ‘hard’ infrastructure projects aim to improve local infrastructure and upgrade existing infrastructure to withstand extreme weather events. ‘Soft’ adaptation or support to farm-level systems target livelihood diversification and productivity. Meanwhile ‘integrated’ sub-projects mix hard and soft adaptation strategies. The sub-projects are administered through grants at different levels: district grants, ward grants, community grants and individual champions. We incorporated ten soft-adaptation, local village, chicken and goat projects, six integrated, and four small-scale hard infrastructure projects.
Fieldwork was conducted between October 2021 and January 2023, and in May 2024. We positioned local people as knowledge holders through informal conversation, observation, and group discussion. Data collection was conducted in the local languages Lozi and/or Tonga, allowing rich and detailed conversations. We conducted a
documentary analysis of SCReBs and other climate-related documents to get background information about the project and the CDCA. We analysed how resilience is approached and supported, and the application of the ILK. We interviewed staff at the MGEE/PPCR: project officers at national, provincial, district and sub-district levels (
n = 25). They included representatives of the
Litunga/King. We convened
group discussions with sub-project participants using an open-ended interview guide (
n = 20). Groups were largely mixed across gender and generation except for the sub-projects that were exclusively run as women’s groups. This helped to obtain information on how groups of people think or feel about strengthening climate resilience and the role (or marginality) of ILK. Altogether, we constituted 20 FGDs (focus group discussions), one per sub-project at the community level in each of the seven study districts. Finally, we used
non-participant direct observation to gain an on-the-spot impression of the state of the sub-projects, allowing informal questions to be posed based on the observations (
Hamilton & Finley 2019).
All data collected from interviews and focus group discussions were coded and analysed using content analysis (
Hsieh & Shannon 2005). We sorted qualitative data using NVivo, creating nodes as thematic areas. Nodes were then analysed manually to explore emphasised elements, and relationships. Analysis focused on narratives around the implementation structure and organisation of the project, resilience building and the role of ILK. Where necessary, we retained qualitative quotes to maintain grounded narratives.
Local perceptions of vulnerability, Lozi spirituality and environmental protection
Droughts and floods were frequently cited extreme weather events experienced by participants since the 1990s. To the Lozi, although there is a long history of environment-related shocks,
‘what is new is the intensity, frequency and severity of climate change’ (Interview, Academic, 2024)
. Climate change is seen as changes to rainfall patterns, changing life and reducing agricultural yields, with opinions that water pollution by the spirit of the river is responsible (
Sampa et al. 2019). The Lozi-speaking people observe a depletion of birds (such as the
linongolo—Openbill Stork), fish (
dona) and plant species. This includes reptiles (such as the
lingongole, a huge imaginary water snake). Participant’s accounts reveal experiences of severe hunger, with crops such as maize and rice drying up during droughts, leading to poor harvest, reduced crop diversity and narrow consumption patterns. They report a high prevalence of livestock diseases, reduced diversity of forest animals, reduced livestock, high temperatures and reduced pasture for livestock. Participants report impacts of reduced water availability on pasture and domestic livestock affecting incomes and food. One participant in Kazungula explained:
‘in these years, poor rains affected our crops, and our environment was dry. We face diseases, shortage of water for our own drinking and pasture for animals’ (FGD, Kazungula District, 2021). Meanwhile, floods reportedly wash away crops such as maize and groundnuts, with further impacts on assets (including domestic animals) and housing infrastructure. For indigenous communities such as the Lozi, there is nothing new about climate change. Such communities have lived with and adapted to climate change for centuries.
Meanwhile, the Lozi have an exceptional systematic structure of authority: from the Litunga to queens of the south and north, and Indunas who act as ministers, and chiefs. It is believed the Litunga is kaongolo kanyambe (the insect of God), Ngochana (the weakest calf)—one needing protection of everyone surrounding him yet he is everything. As with
Mamati (2024), from childhood, every member of the society is taught customs for protecting the landscape, thereby protecting the Ngochana. He is the unifier, the link to Nyambe (God). The wealth of the Litunga is not material accumulation per se, but all that is under the earth. He is the co-ruler with predecessors who are continuously consulted on key decisions by the Lingomboli (priests)—those with eyes. The Lingomboli tend the burial sites of predecessors and perform unseen duties (not in the public domain) and communicate spiritually.
Oral histories from our participants reveal diverse but important myths surrounding the origins of the Lozi tribe. One belief is that the tribe starts with
Nyambe (the sun god) who descends from the heavens into the Barotseland (
Kapambwe 2018).
Nyambe is displeased with
Kamunu (the human being) for killing his children—animals and fish.
Nyambe is unhappy when humans kill his own creation and returns to the unknown. Here,
Nyambe effectively stamps the relational and conservationist identity of the Lozi, including spiritual attachment to landscape (see also Mamati
2024 in this Special Issue). Interviews with one
Induna (chief’s representative) as one of the knowledge holders reveal
Nyambe is the maker of everything, including the earth. The Lozi-speaking people believe in him, but do not see him. He is known as ‘he who does not talk’, somebody you do not speak to directly, the highest God.
3 For the Lozi-speaking people, the centrality of natural resource management points to this wisdom. This cultural and spiritual value links the Lozi with their ‘God and environment.’ Taboos and myths have been used to restrict the use of natural resources. The
Lingomboli can speak with the god of rain to calm the weather, including storms and heavy waves in the Zambezi River. Protection of species follows clear beliefs. There are trees, forests and certain species for the
Litunga/Ngochana—and no one should be found harvesting these. This includes islands—breeding spaces for various species—along the Zambezi River. For instance, some plant species with utilitarian value are not allowed to be cut without permission from the
Litunga. There are taboos and myths related to poaching (for example, eland, lion and leopard), and spiders, pythons, fish (for example, perch/
mbunda); (silver catfish/
lubango) and plants. As part of the
Litunga’s species,
‘the tail of the eland forms part of the instruments of power. Any sick or dead animal should be reported’ (
Induna 2024). Eating habits such as around consumption of eggs of birds and hunting of geese or crocodiles require permission (
Milupi et al. 2020).
There is evidence that communities deploy diverse strategies to navigate climate challenges, revealing a deep sense of local ecological knowledge about their environments. Intra-community and intra-household relationships are crucial during
munda (floods) and
linanga (drought). Reliance on alternative sources of firewood to avoid deforestation, such as using
man’ele (ligneous grass); changing seed regimes for crops such as cassava; seasonal movement of cattle from the floodplains during floods to the upper land and back to the floodplains when water levels subside are part of Lozi traditional practices. The plains experience flood inundation annually and people tend to move to the upland in the rainy season and then come back to the floodplain when the inundation recedes.
Kuomboka—meaning ‘to get out of water’—celebrates the move of the
Litunga from his compound at
Lealui in the Barotse floodplain to
Limulunga on higher ground. The return trip is usually held in August with a less publicised journey called the
Kufuluhela. Livelihoods among the Lozi are intricately linked to these environmental dynamics (Figure
1).
Figure 1.
The Litunga’s boat/barge—known as Nalikwanda—during the Kuomboka (‘get out of water’) ceremony. The ancient ceremony cerebrates the move of the Litunga from his summer home ‘Lealui’ in the flooded villages of the Barotse floodplain to his winter home in Limulunga on the higher ground. The Litunga stays there until the flood subsides (photograph: Mizinga Mahalihali 2023).
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Over time, community members engaged in migratory practices across seasons, practised agroforestry and management of degraded farming areas and elements around ecosystem services and resource utilisation. Meanwhile,
kuloba sitaka 4—a collective bird cropping exercise—ensures sustainable harvesting of birds along the Zambezi River, avoiding overexploitation. Here, certain sanctuaries are designated for harvest on a particular day.
Kutulisa—rotational grazing—allows regeneration of vegetation and avoids overgrazing (
Milupi et al. 2020). There are strategies around the role and importance of social networks and relational wellbeing, spirituality and taboos, including rainwater harvesting and rainmaking. In some cases, changing consumption patterns were also applicable (see also
Makondo & Thomas 2018). All these elements relate deeply to wisdom, techniques and practices relied upon over many years and ones that remain relevant today. However, these have been peripheral to donor-driven interventions, raising challenges for the sustainability of climate interventions.
When good intentions are not enough—CDCA designs and climate needs
Participants across the selected donor projects clearly identified climate change links as relevant intervention areas. Although one key informant argued:
‘a clear understanding of these climate risks has allowed selection of appropriate sub-projects’ by the participants (Provincial Respondent, 2022), analysis reveals that actual project selection was shaped largely by the Participatory Adaptation Implementation Manual and the guidance of district and provincial level officials—also known as Climate Risks and Adaptation Facilitators (CRAFTS)—and not ILK systems. CDCA was supposed to leverage on ILK in the design. The ‘community’ in the CDCA is supposed to mean integration of local knowledge and agency. However, actual implementation structure privileges project and funding guidelines/interests, with local groups integrated only as holders of sub-grants (Figure
2). We found no clear pathways through which the design examined ILK and awareness of climate change and related environmental risks. Also missing were conversations about the local framings of vulnerability—one we find to be a fluid concept among the Lozi. This is worsened by projects being too small to generate meaningful livelihood impacts, resilience and improve incomes (for example, gardening or tending livestock) (Figure
2).
Figure 2.
Implementation structure of the CDCA projects (authors).
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Figure 3.
Donor-funded solar-powered small-scale garden irrigation system (photograph by Chrispin Matenga).
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Analysis revealed inadequate integration of ILK into the type of projects necessary in host communities—ones that can respond to the perceived level of vulnerability and build on previous traditional practices. Material and lived aspects of human culture, including shared narratives did not form part of the central organising elements of CDCA (see
Manda 2023). Instead, project implementers relied on the project implementation manual as the central mobilising feature of community projects (Figure
3).
A focus on the project implementation manual placed donor funds and decision making in the hands of community members,
‘as long as this is within the project requirements’. And that in so doing,
‘this approach strengthens community voice to demand greater accountability of themselves and the institutions that are relevant to strengthening livelihoods’ (District Project Officer, 2022). However, community voice in the project relates to decisions by committees. As a result, local groups rarely called for greater accountability even within their own groups or committees—even when suspicions of financial misappropriation emerged. This misalignment is crucial for the sustainability of adaptation projects. Consequently, participants failed to explicitly steer the project in their own direction. Procurement of project services was frequently cited as difficult for members to navigate due to committee members dominating decision-making, and non-availability of procurement and support services locally. In most cases, wider group members (outside project management committees (PMCs)) were excluded from key procurement and project decision-making, raising suspicions of capture. These processes can thus be disempowering. One
Induna expressed an opinion that CDCA designs including other interventions, such as those related to wildlife protection, have tended to tamper with preexisting traditions rather than build on them, and that the Lozi-speaking people face constant political pressures (see also
Manda & Banda 2023).
Marginality of indigenous and local knowledge
We reflect on the centrality of the CDCA project approach across two broad spheres and how this leads to the marginality of IKL.
False narrative of CDCA as empowerment of communities
National and district interviewees frequently argued that CDCA was an empowering exercise, but empowerment itself was narrowly framed around project management and funding aspects. We found three important elements.
The first frame relates to group formation and selection of sub-projects. CDCA arguably enabled selection of sub-projects based on community consultation. However, sub-projects were identified by and through pre-existing local groups during participatory planning processes for climate risk and adaptation, assisted by CRAFTs. Some government officers argued that local communities’ involvement in what was characterised as participatory planning processes allowed community members themselves to analyse climate risks, prioritise problems and select responses as ‘shared goals’ (PPCR Interview, 2022). Empowerment is framed around group participation as opposed to processes and capacity across groups, including intra-group negotiations of resource rights and integration of ILK. This is even though selection of projects built on pre-existing groups (for example, Village Savings Groups or Cooperative groups). Processes did not produce new cohorts based on local framings of climate risks and vulnerabilities. Project implementers justified this as enhancing continuity, allowing opportunity to build on pre-existing ‘workable’ partnerships, and enabling ownership. However, previous groups were not mooted as strengthening climate resilience. Interestingly, rather than integration of ILK, project implementers were concerned that groups continued to express a general lack of business culture and market awareness in CDCA sub-projects. Consequently, groups continuously face governance challenges, affecting sustainability of the projects.
Second is resources distribution to community groups—decentralisation logic. Across the sub-projects, the CDCA approach granted participants direct access and control over planning decisions and investment resources, but these centred on pre-approved projects. Whereas project management committees (PMCs) were solely responsible for the withdrawal of sub-grants, interviews revealed a lack of capacity among grantees to sustainably utilise the funds. A quick decision to include district-level technical staff as signatories to some of the project bank accounts highlights the lack of capacity. We found financial accounting challenges across all projects. In Kaoma’s Lunyati North Drip Irrigation Project, group discussion revealed disagreements between members and the treasurer on record keeping. Whereas the treasurer claimed there existed records of all activities, members were not privy to these records (similar to experiences in Kazungula’s Puzukwa Irrigation Scheme). Members had little information on how much the project cost, arguing, ‘when it comes to money, it is the chairlady who knows about that’ (FGD Participant, 2021). This shows that the flow of resources to community groups did not automatically translate into improved downward accountability.
Third is inclusive governance mechanisms. CDCA is often credited with building transparency and accountability. However, projects assumed homogeneity in the governance process, although ‘membership include[s] people living with HIV, widows, and the aged’ (FGD Interview, 2021). Analysis reveals an uncritical reflection of the basis and terms on which local groups/individuals were included in these projects, including what they are able or unable to do.
Narrow perception of capacity building
CDCA has been promoted as pathways to building local capacity across two areas. First is financial management and procurement. Generally, disbursement of funds to sub-projects is through a project bank account depending on accountability of previous disbursements. Participating groups were trained in basic financial literacy and accountability. While it is a requirement for committees to produce regular financial reports, many group members did not receive regular updates on finances. Analysis revealed that across projects, financial matters were poorly communicated to group members. PMCs organise, plan, implement and account for funds, including procurement of goods and services (operations and management). They procure goods and services for the community sub-projects. However, community groups still relied on District Officers in advertising for and procuring small works or services at community level. While some PPCR technical experts help monitor projects, services from government line departments, such as Water Engineering, Veterinary, or Agriculture, and in some cases agro-dealers, were missing, leaving projects poorly supported. Thus, the majority of sub-projects required continued technical and non-technical support (for example, water point committees and related tap attendants and pump operators), but these requirements added an extra layer of work for communities supposed to be adapting to climate change. The so-called community-level groups became embedded in the government procurement chain and bureaucracy. In some cases, participating groups procured faulty products, affecting implementation. Examples include non-durable solar pumps and faulty installations that leave community groups without water for project activities and non-durable pond liners for some fish farming sub-projects.
Some of these relate to inadequate funding to line departments, which affected backstopping activities. District government officers revealed a lack of financial resources to undertake frequent support and extension services (for example, transport). As a result, CDCA project activities in some cases were treated as auxiliary activities even where projects had been handed over to support line ministries. In Kazungula, one District Administrative Officer argued ‘operational funds from the project office are insufficient and sometimes inconsistent for us to offer continued support’. Given that funding support was given to District staff and was complementary to already existing government funding, officers expressed opinions that more sensitivity about the role and importance of field-level Government Extension staff closer to project sites was needed. There are several examples of poor support from government departments. The study finds irrigation projects such as Mwandi Irrigation Scheme had poor links and support from the Department of Water Affairs, as water systems were not working to capacity. The project has four water tanks each with a capacity of 10,000 litres, but faulty designs by the private contractor meant that only two tanks were filling up (20,000 litres) to capacity, leading to drying of crops and underutilisation. Whereas the named contractor was supervised by the Department of Water Affairs, the department itself struggled to offer after-services. Failure to operate to full capacity further discouraged group membership and group-based adaptation activities. There are similar experiences in projects dealing with livestock (for example, pigs, goats and chickens) where members complained their animals either died or were diseased—placing blame on the Department of Veterinary Services. The Department of Fisheries was also cited as offering insufficient support. Overall, and for most part, capacity building appears general as opposed to climate and livelihood related capacity building that capitalises on cultural skills and practices.
How can ILK be organised to expand inventories of adaptation possibilities?
We asked study participants at what point CDCA strengthens climate resilience. Officers argued that CDCA provided relevant needs assessment, including aspects of climate-resilient activities as ‘key intervention areas for climate change adaptation by grantees’ (District Interview, 2022). They added that it finds relevance in localising a problem-solving approach which speaks to ‘real’ climate risks faced by communities. However, which problems were being addressed and for what vulnerabilities was less clear. This shows that currently donor-driven CDCA is technically inadequate to address climate resilience from a social and cultural perspective. Some national experts within NPCU agreed ‘with CDCA, communities do not have all the technical know-how and expertise to find effective solutions to local challenges’. Analysis reveals that CDCA projects did not fully recognise the role and importance of ILK in the design and implementation of projects. Analysis reveals CDCA did not sufficiently enable local structures to be effective in addressing climate needs and integrating ILK. A reliance on local structures such as Ward Development Committees reveals the mismatch between project expectations and challenges on the policy–ILK intersection.
Marginalisation of ILK means that local needs are poorly articulated, and projects are poorly linked to local perceptions of vulnerabilities and response pathways. For instance, in some parts of the western province and among the Lozi-speaking people, floods are not perceived as a source of vulnerability but as an opportunity as they have over time found adaptation pathways through migratory practices. CDCA arguably enhances efficiency and cost-effectiveness where funds are remitted directly into beneficiary accounts, and where ‘financial management guidelines are strictly adhered’ (Mwandi FGD 2022), but this effectively takes away a layer of responsibility from project developers and government officers and places it on community members.
Our analysis reveals that the application of the CDCA faces four main challenges. First, despite devolving responsibility to procure goods and services at local level, there are still some capacity challenges in this area. Second, majority projects are mooted in isolation to other critical support resources and services, such as water and extension services (for example, Lyambayi Piggery Project in Sioma District and Matoka Women’s Goat Project in Kazungula District), limiting engagement with different knowledges. Third and related to the second is that there is little coordination on technology issues between local communities and support service organisations. Small-scale water infrastructure projects have relied on solar-powered technology to abstract water, for which the participating communities demonstrated limited knowledge about technical specifications of the equipment itself or backup maintenance. Finally, the scale of most CDCA sub-projects reviewed is too minute to engender meaningful adaptation, livelihoods and resilience. Sub-projects frequently registered low production for the kind of effort and resources expended on the community groups. These elements remain peripheral to climate adaptation needs, meaning the introduction of CDCA might have a devastating impact on socio-cultural dimensions of wellbeing.
The potential to expand inventories of possibilities for adaptation at the policy–ILK interface exist and is crucial for sustainability and equity of adaptation measures, but this is hindered by design elements that continue to privilege scientific knowledge and technical assumptions of adaptation. CDCA ignores the centrality of landscapes—scenery, history and culture that shapes human–nature relations (see also
Mamati 2024). In Sioma District, for instance, participants are in partnership with the Ministry of Agriculture to receive weather reports from the Zambia Meteorological Department. As one key informant argued,
‘farmers are able to consult the department of agriculture for the interpretation of weather data’ (Interview Sioma, 2022). However, in most areas the CDCA did not lead to progressive and relevant partnerships that could help build on existing productive activities as part of ILK. In Mwandi District, participants expressed opinions that
‘there is need for a technical expert to look at our water challenges’. There are also calls for partnerships in Kaoma District on fish seed production and Nkeyema District on support to curb poultry diseases. These avenues can help intersect policy and ILK and expand adaptation possibilities for local people.