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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Sustain. Food Syst.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Sustainable Food Systems</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Sustain. Food Syst.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">2571-581X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fsufs.2026.1736719</article-id>
<article-version article-version-type="Version of Record" vocab="NISO-RP-8-2008"/>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Exploring challenges and agroecological solutions for vegetable production in semi-arid Turkana County, Kenya</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Aule</surname> <given-names>Alex Eeman</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<contrib contrib-type="author">
<name><surname>Werner</surname> <given-names>Aspasia</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
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<contrib contrib-type="author">
<name><surname>Jordan</surname> <given-names>Irmgard</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
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<contrib contrib-type="author">
<name><surname>Keding</surname> <given-names>Gudrun B.</given-names></name>
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<aff id="aff1"><label>1</label><institution>Department of Physical Sciences and Biological Sciences, Turkana University College (TUC)</institution>, <city>Lodwar</city>, <country country="ke">Kenya</country></aff>
<aff id="aff2"><label>2</label><institution>Department of Nutritional Science, Chair of International Food and Nutrition Security, Justus-Liebig University Giessen</institution>, <city>Senckenbergstra&#x000DF;e</city>, <country country="de">Germany</country></aff>
<aff id="aff3"><label>3</label><institution>Bioversity International, Food Environment and Consumer Behavior Research Group</institution>, <city>Nairobi</city>, <country country="ke">Kenya</country></aff>
<author-notes>
<corresp id="c001"><label>&#x0002A;</label>Correspondence: Alex Eeman Aule, <email xlink:href="mailto:alexeemanaule@gmail.com">alexeemanaule@gmail.com</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-03-04">
<day>04</day>
<month>03</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>10</volume>
<elocation-id>1736719</elocation-id>
<history>
<date date-type="received">
<day>31</day>
<month>10</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>06</day>
<month>02</month>
<year>2026</year>
</date>
<date date-type="accepted">
<day>09</day>
<month>02</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2026 Aule, Werner, Jordan and Keding.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Aule, Werner, Jordan and Keding</copyright-holder>
<license>
<ali:license_ref start_date="2026-03-04">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</license-p>
</license>
</permissions>
<abstract>
<sec>
<title>Introduction</title>
<p>Agroecological farming is increasingly promoted as a climate-smart strategy for drylands, yet evidence on its effectiveness, acceptability, and sustainability in pastoral and agropastoral contexts remains limited. This study examined constraints to vegetable production and assessed the feasibility of selected agroecological practices in Turkana County, Kenya.</p>
</sec>
<sec>
<title>Methods</title>
<p>The study combined 12 gender-disaggregated Focus Group Discussions (FGDs) with Trials of Improved Practices (TIPs). FGDs identified locally relevant agroecological techniques, which were subsequently tested by 50 households. Two follow-up visits conducted two weeks apart assessed uptake, adaptations, and willingness to continue.</p>
</sec>
<sec>
<title>Results</title>
<p>Key constraints identified during FGDs included pest infestation (83%), water scarcity (75%), and poor soil health (67%). The most adopted practices during TIPs were animal manure (59%), intercropping (51%), and use of ash (45%). Bottle irrigation (2%) showed minimal adoption due to material and technical limitations. Adoption rates were higher among agropastoralists than pastoralists. By the third visit, 79% of farmers were willing to continue at least one practice.</p>
</sec>
<sec>
<title>Discussion</title>
<p>The findings highlight that adoption of agroecological practices in semi-arid drylands is shaped by practical feasibility, resource availability, and livelihood strategies. TIPs proved effective for identifying context-appropriate, low-cost practices aligned with farmers&#x00027; needs and constraints. These results provide empirical support for participatory, farmer-led evaluation approaches in dryland agroecology.</p>
</sec></abstract>
<kwd-group>
<kwd>agroecological approaches</kwd>
<kwd>agropastoralists</kwd>
<kwd>focus group discussion</kwd>
<kwd>trials of improved practices</kwd>
<kwd>vegetables</kwd>
</kwd-group>
<funding-group>
<award-group id="gs1">
<funding-source id="sp1">
<institution-wrap>
<institution>Stiftung fiat panis</institution>
<institution-id institution-id-type="doi" vocab="open-funder-registry" vocab-identifier="10.13039/open_funder_registry">10.13039/501100011087</institution-id>
</institution-wrap>
</funding-source>
</award-group>
<award-group id="gs2">
<funding-source id="sp2">
<institution-wrap>
<institution>Arbeitsgemeinschaft f&#x000FC;r Tropische und Subtropische Agrarforschung</institution>
<institution-id institution-id-type="doi" vocab="open-funder-registry" vocab-identifier="10.13039/open_funder_registry">10.13039/100022852</institution-id>
</institution-wrap>
</funding-source>
</award-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This research was funded by Fiat Panis Foundation &#x00026; ATSAF e.V. Junior Scientist Tandem (JST) Program for Master&#x00027;s students and was implemented by Georg-August University Goettingen, Turkana University and Alliance of Bioversity International and CIAT under the scope of the FEnDrylands Project. The authors have no conflict of interest and would like to thank in particular all farmers who spent their time on this project and who were available for the different discussion and interview rounds as well as the final workshops and were willing to share their views with the researcher.</funding-statement>
</funding-group>
<counts>
<fig-count count="5"/>
<table-count count="5"/>
<equation-count count="0"/>
<ref-count count="19"/>
<page-count count="12"/>
<word-count count="6609"/>
</counts>
<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Agroecology and Ecosystem Services</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="s1">
<label>1</label>
<title>Introduction</title>
<p>Turkana County, Kenya experiences low rainfall, poor soils, and constant water scarcities which makes it one of the most vulnerable drylands to the effects of climate change. These environmental challenges has limited the production of vegetables and has worsened the threat of food shortages (<xref ref-type="bibr" rid="B4">Hossain et al., 2020</xref>). In addition, studies have emphasized that the agriculture systems of drylands are particularly vulnerable to climate changes and need new strategies to withstand the advanced effects of global warming (<xref ref-type="bibr" rid="B14">Nicol&#x000E9;tis et al., 2019</xref>).</p>
<p>One promising approach to solving this challenges is the implementation of agroecological principles that integrate, among others, ecological methods into farming (<xref ref-type="bibr" rid="B1">Altieri and Nicholls, 2020</xref>). However, there is insufficient evidence on the suitability of such methods in dryland ecosystems (<xref ref-type="bibr" rid="B12">Mockshell and Kamanda, 2018</xref>).</p>
<p>Additionally, previous studies have placed more emphasis on technical recommendations than on participatory evaluation, ignoring the ways in which local farmers develop, apply, and continue to modify the existing techniques to fit their particular socio-ecological contexts. Therefore, this study aims to contribute to closing the following three gaps:</p>
<list list-type="bullet">
<list-item><p>Limited farmer-led evaluation of agroecological practices in semi-arid environments.</p></list-item>
<list-item><p>Absence of data from participatory studies, like Trials of Improved Practices (TIPs) that evaluate the viability and sustainability of the existing techniques in East African drylands.</p></list-item>
</list>
<p>Informed by these gaps, the research asks the following questions:</p>
<list list-type="simple">
<list-item><p>1) What are the agronomic, ecological, and socio-economic challenges faced by farmers in arid and semi-arid areas in vegetable production systems?</p></list-item>
<list-item><p>2) Which agroecological practices are used or tested by local farmers to improve vegetable production?</p></list-item>
<list-item><p>3) How sustainable and acceptable are the recommended agroecological practices, shown i.e. by the adoption rate and willingness to continue with the practice, for vegetable production in Turkana County, Kenya?</p></list-item>
</list>
</sec>
<sec id="s2">
<label>2</label>
<title>Literature review</title>
<p>Globally, agroecology has been acknowledged as a viable farming practice in vulnerable environments facing persistent challenges such as water scarcity, increasing pest pressure and soil degradation (<xref ref-type="bibr" rid="B2">FAO, 2023</xref>; <xref ref-type="bibr" rid="B3">HLPE, 2019</xref>). Previous farming practices, such as irrigation and rain-fed farming, have proven to be largely unsustainable in these regions and as a result, agroecology aims to increase the resilience of farms while integrating the social, environmental, and indigenous dimensions to ensure that farming does not diminish those aspects.</p>
<p>Across the East African region, agroecological techniques, particularly in dryland farming, achieve high levels of productivity and ecological resilience. For instance, farmers in Kenya, i.e., in Kiambu and Makueni County Agroecology Living Landscapes, use bio pesticides, intercropping, and</p>
<p>Farmyard or and compost manure as part of their integrated strategies for managing soil, water, and pests (<xref ref-type="bibr" rid="B10">Kuria et al., 2024</xref>). Additional data from Embu County indicates that cowpea productivity has increased in dryland environments using moisture-regenerative techniques including mulching and intercropping cereals and legumes. However, the persistent problem of input unavailability continues to limit such increases (<xref ref-type="bibr" rid="B13">Mogaka, 2023</xref>). When considered collectively, these studies show that agroecology is not only good for the environment but also flexible enough to provide long-term resilience in dryland farming systems.</p>
<p>Turkana County in northern Kenya represents one of the most difficult agricultural environments globally. Recurrent droughts, depleted soils, and acute water scarcity severely constrain agricultural livelihoods and threaten household food security (<xref ref-type="bibr" rid="B11">Mawaa, 2022</xref>; <xref ref-type="bibr" rid="B19">World Vision, 2024</xref>). In such conditions, agroecology holds considerable potential for improving both food security and ecological sustainability. However, important knowledge gaps persist. There is limited understanding of the specific challenges that discourage farmers in dryland areas such as Turkana from fully adopting agroecological practices (<xref ref-type="bibr" rid="B9">Kirui et al., 2023</xref>). In addition, documentation remains sparse on the agroecological techniques already in use locally, as well as how farmers prioritize and adapt these practices in their local environment (<xref ref-type="bibr" rid="B10">Kuria et al., 2024</xref>). In addition, few studies have identified how communities evaluate if such practices represent durable resilience or are simply temporary coping strategies.</p>
<p>To fill these gaps, this study uses the Sustainable Livelihoods Framework (SLF) as its main conceptual lens. The SLF focuses on the various forms of capital that households might combine to maintain and improve their standard of living, including natural, human, social, physical, and financial capital (<xref ref-type="bibr" rid="B18">Scoones, 1998</xref>). Using this framework allows the study to move beyond simply listing the agro ecological practices that farmers use. It also helps to understand the local resources people have, the livelihood strategies they depend on, and the social and cultural factors that shape how and why these practices are adopted and sustained. In this way, the framework supports the main aims of the study: identifying key production challenges, documenting local agro ecological practices, and assessing how suitable and sustainable these practices are for pastoral and agro pastoral communities in Turkana County.</p>
</sec>
<sec id="s3">
<label>3</label>
<title>Materials and methodology</title>
<sec>
<label>3.1</label>
<title>Study area and schedule</title>
<p>The study was carried out between the month of September 2023 and April 2024 in the two community units Kabulokor and Atala Kamusio that are located in Loima sub-county, Turkana County, Kenya (<xref ref-type="fig" rid="F1">Figure 1</xref>). This region is primarily semi-arid and experiences unpredictable rainfall and families are vulnerable to severe droughts, limited food supplies, and limited sources of income (<xref ref-type="bibr" rid="B8">Kenya National Bureau of Statistics (KNBS), 2019</xref>).</p>
<fig position="float" id="F1">
<label>Figure 1</label>
<caption><p>Map of Kenya, showing the study areas Kabulokor and Atala kamusio community units in Turkana county. (Map created using the free and open source QGIS, version 3.44.5-Solothurn).</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fsufs-10-1736719-g0001.tif">
<alt-text content-type="machine-generated">Map of Kenya with a shaded region in the northwest indicating a specific area of interest. Two red dots are labeled Atala Kamusio and Kabulokor within this shaded region, shown with arrows pointing to each location.</alt-text>
</graphic>
</fig>
<p>Kabulokor (home to approximately 253 households with an average family size of about five persons (<xref ref-type="bibr" rid="B8">Kenya National Bureau of Statistics (KNBS), 2019</xref>) is mainly occupied by agropastoral households who grow some crops alongside herding. In contrast, Atala Kamusio which has about 246 households with a similar average family size to Kabulukor (<xref ref-type="bibr" rid="B8">Kenya National Bureau of Statistics (KNBS), 2019</xref>) has historically relied almost entirely on livestock. However, as grazing resources decline in Atala Kamusio, pastoralists have just gradually introduced short-season, drought-tolerant vegetable production as an alternative and complementary livelihood strategy in response to declining pastoral resources and changing climate conditions.</p>
<p>These two community units were purposively selected for this study because both communities carry out vegetable production, despite their differing livelihood systems. This presented a unique opportunity to understand how agroecological methods are adapted, implemented, and learnt by dryland communities with diverse livelihoods.</p>
</sec>
<sec>
<label>3.2</label>
<title>Study design and data collection</title>
<p>The research used a mixed method design, mixing qualitative data collection with a formative research approach and worked in three clear steps: (1) Focus Group Discussions, (2) Trials of Improved Practices (TIPs), and (3) Reflection Workshops. <xref ref-type="fig" rid="F2">Figure 2</xref> presents the overall sequence of these three phases, illustrating the progression from FGDs to TIP implementation and, finally, reflection workshops in each community.</p>
<fig position="float" id="F2">
<label>Figure 2</label>
<caption><p>Flow diagram illustrating the step-by-step process of data collection between September 2023 and April 2024 in Turkana County, Kenya.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fsufs-10-1736719-g0002.tif">
<alt-text content-type="machine-generated">Phase 1 involves focus group discussions led by the first author to gather input from selected participants.</alt-text>
</graphic>
</fig>
</sec>
<sec>
<label>3.3</label>
<title>Participant flow across study phases</title>
<p>Participant recruitment, progression, and attrition across the different study phases are summarized in <xref ref-type="table" rid="T1">Table 1</xref>. This overview provides transparency regarding participant numbers, selection processes, and reasons for drop-out.</p>
<table-wrap position="float" id="T1">
<label>Table 1</label>
<caption><p>Participant recruitment, progression, and attrition across FGDs, TIPs visits, and reflection workshop in two study sites in Turkana, Kenya.</p></caption>
<table frame="box" rules="all">
<thead>
<tr>
<th valign="top" align="left"><bold>Study phase</bold></th>
<th valign="top" align="center"><bold>Kabulokor (<italic>n</italic>)</bold></th>
<th valign="top" align="center"><bold>Atala Kamusio (<italic>n</italic>)</bold></th>
<th valign="top" align="center"><bold>Total (<italic>n</italic>)</bold></th>
<th valign="top" align="left"><bold>Notes</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">FGDs participants</td>
<td valign="top" align="center">68</td>
<td valign="top" align="center">72</td>
<td valign="top" align="center">140</td>
<td valign="top" align="left">12 gender-disaggregated FGDs, 6 per study site</td>
</tr>
<tr>
<td valign="top" align="left">Selected for TIPs</td>
<td valign="top" align="center">25</td>
<td valign="top" align="center">25</td>
<td valign="top" align="center">50</td>
<td valign="top" align="left">Purposive &#x0002B; lottery selection</td>
</tr>
<tr>
<td valign="top" align="left">TIPs Visit 1</td>
<td valign="top" align="center">24</td>
<td valign="top" align="center">25</td>
<td valign="top" align="center">49</td>
<td valign="top" align="left">1 declined consent (migration)</td>
</tr>
<tr>
<td valign="top" align="left">TIPs Visit 2</td>
<td valign="top" align="center">19</td>
<td valign="top" align="center">19</td>
<td valign="top" align="center">38</td>
<td valign="top" align="left">Attrition due to migration, lack of water and inputs</td>
</tr>
<tr>
<td valign="top" align="left">TIPs Visit 3</td>
<td valign="top" align="center">19</td>
<td valign="top" align="center">19</td>
<td valign="top" align="center">38</td>
<td valign="top" align="left">No further attrition</td>
</tr>
<tr>
<td valign="top" align="left">Reflection workshops</td>
<td valign="top" align="center">37</td>
<td valign="top" align="center">33</td>
<td valign="top" align="center">70</td>
<td valign="top" align="left">Farmers, leaders and extension officers</td>
</tr></tbody>
</table>
<table-wrap-foot>
<p>FGD, Focus Group Discussion; TIPs, Trials of Improved Practices.</p>
</table-wrap-foot>
</table-wrap>
<p>The TIPs catalog of improved practices and TIPs tools were pre-tested with farmers at Napuu Farm in Lodwar for 2 days. Prior to data collection, the note-taker as well as the six enumerators received a 2 day training how to advise on the tools. Similarly, the follow-up TIPs questionnaire was pre-tested with Turkana University College students, and this helped the research team refine structure of the questions, their flow, and language use.</p>
</sec>
<sec>
<label>3.4</label>
<title>Data management and analysis</title>
<p>A detailed overview of the data management and analysis process is shown in <xref ref-type="fig" rid="F3">Figure 3</xref>. The figure outlines key steps, for thematic development, coding structures, reliability checks, and the integration of qualitative and quantitative findings.</p>
<fig position="float" id="F3">
<label>Figure 3</label>
<caption><p>Overview of the data management and analysis steps, including thematic development, coding structure, reliability checks, and integration of qualitative and quantitative findings.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fsufs-10-1736719-g0003.tif">
<alt-text content-type="machine-generated">Flowchart illustrating a mixed methods analysis process, starting with audio recording and English transcription of FGDs and workshops, followed by thematic qualitative data analysis, rigor checks, quantitative data analysis in Excel, and final integration through convergence analysis.</alt-text>
</graphic>
</fig>
</sec>
<sec>
<label>3.5</label>
<title>Examples of final coding categories and analytical themes</title>
<p>In order to enhance transparency of the qualitative analysis, <xref ref-type="table" rid="T2">Table 2</xref> provides examples of final coding categories and analytical themes generated from the workshop discussions. The coding was done using MAXQDA software, allowing the study to systematically organize the discussions into meaningful themes. This presentation focuses on how the themes were developed, rather than the results themselves.</p>
<table-wrap position="float" id="T2">
<label>Table 2</label>
<caption><p>Sample of final coding categories and analytical themes.</p></caption>
<table frame="box" rules="all">
<thead>
<tr>
<th valign="top" align="left"><bold>Final Theme</bold></th>
<th valign="top" align="left"><bold>Description</bold></th>
<th valign="top" align="left"><bold>Example sub-codes</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Water and resource constraints</td>
<td valign="top" align="left">Factors limiting vegetable production and trial implementation</td>
<td valign="top" align="left">Water scarcity, seed availability, fencing materials</td>
</tr>
<tr>
<td valign="top" align="left">Knowledge and extension access</td>
<td valign="top" align="left">Sources, gaps, and modes of agronomic knowledge</td>
<td valign="top" align="left">Extension services, peer learning, prior experience</td>
</tr>
<tr>
<td valign="top" align="left">Household labor and gender dynamics</td>
<td valign="top" align="left">Organization of labor and decision-making within households</td>
<td valign="top" align="left">Gendered task allocation, time constraints</td>
</tr>
<tr>
<td valign="top" align="left">Perceived benefits and risks of practices</td>
<td valign="top" align="left">Farmers&#x00027; evaluation of agroecological practices tested</td>
<td valign="top" align="left">Yield improvement, labor demand, water efficiency</td>
</tr></tbody>
</table>
</table-wrap>
</sec>
<sec>
<label>3.6</label>
<title>Ethical considerations</title>
<p>Ethical approval for the study was obtained from the School of Graduate Studies, Turkana University College, and the Institutional Review Board (IRB) of the Alliance of Bioversity International and CIAT (IRB51). Additional clearance was granted by the National Commission for Science, Technology and Innovation (NACOSTI) under License No. NACOSTI/P/23/29342.</p>
<p>Before data collection began, all participants were informed about the purpose and objectives of the study. Participation was entirely voluntary, and individuals were free to provide or decline informed consent, or to withdraw at any stage without any consequences. Throughout the study, participant confidentiality was ensured by safeguarding names, notes, and audio recordings.</p>
</sec>
</sec>
<sec id="s4">
<label>4</label>
<title>Results and findings</title>
<sec>
<label>4.1</label>
<title>Results from focus group discussions</title>
<sec>
<label>4.1.1</label>
<title>Distribution of FGD participants by gender and location</title>
<p>A total of 140 participants took part in the FGDs across the two study community units, with a near-equal representation of both women and men. This gender balanced participation made it possible to gather insights from both men and women in the agropastoralists households of Kabulokor (33 women and 35 men participating, 68 participants in total) and pastoralist households of Atala Kamusio (36 women and men each, 72 in total). There was thus nearly equal number of participation for pastoralists and agropastoralists community units.</p>
</sec>
</sec>
<sec>
<label>4.2</label>
<title>Challenges for growing vegetables from the farmer&#x00027;s perspective</title>
<p>Findings from FGDs and follow-up visits revealed that farmers faced a combination of agronomic, ecological, and socio-economic constraints. Participants consistently emphasized water scarcity, destruction of crops by free-roaming livestock, and limited access to quality seeds as the most pressing barriers to production. Although FGDs are primarily qualitative, we report the frequency with which these themes were mentioned because this information was used to prioritize practices for the subsequent TIPs. Quantitative data from follow-up visits provided additional confirmation of these trends. The main challenges identified by farmers are summarized in <xref ref-type="fig" rid="F4">Figure 4</xref>.</p>
<fig position="float" id="F4">
<label>Figure 4</label>
<caption><p>Agronomic, ecological and socioeconomic challenges for growing vegetables as mentioned by farmers during 12 focus group discussions.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fsufs-10-1736719-g0004.tif">
<alt-text content-type="machine-generated">Bar chart illustrating percentages of focus group discussions (twelve FGDs) mentioning different farming challenges: pest infestation eighty-three percent, poor soil health sixty-seven percent, lack of access to quality seeds fifty-eight percent, water scarcity seventy-five percent, destruction by animals fifty percent, and limited market access thirty-three percent. Bars are color-coded: blue for agronomic, orange for ecological, and gray for socio-economic challenges.</alt-text>
</graphic>
</fig>
<p>Pest infestation and poor soil health were the most severe agronomic challenges, while water scarcity the most critical ecological limitation. Limited access to quality seeds, crop destruction by free roaming livestock was a limitation mentioned in half of the FGD. Market access was a constraint mentioned by one third, only.</p>
<p>One participant from Atala Kamusio explained,</p>
<disp-quote><p>&#x0201C;<italic>None of our farms have a consistent supply of water. We can only obtain rainwater when it rains.&#x0201D;</italic></p></disp-quote>
<p>Similarly, a farmer from Kabulokor noted,</p>
<disp-quote><p>&#x0201C;<italic>We want to grow more vegetables, but getting quality seeds is a challenge. Sometimes we have to travel far to the agro-vets in Lodwar.&#x0201D;</italic></p></disp-quote>
<p>Based on these prioritized challenges, TIPs were designed to focus on low-cost soil fertility management, pest control, and improved water-use efficiency, while remaining compatible with local livelihood systems and available resources.</p>
</sec>
<sec>
<label>4.3</label>
<title>Adoption of selected agroecological practices</title>
<sec>
<label>4.3.1</label>
<title>Adoption patterns by livelihood system</title>
<p>Adoption patterns differed between agropastoralists and pastoralists households, reflecting variations in resource availability and prior farming experience. It is important to note that the study did not aim to directly compare the two systems; rather, these observations describe how each group adapted and sustained agroecological practices within their livelihood context <xref ref-type="table" rid="T3">Table 3</xref>.</p>
<list list-type="bullet">
<list-item><p>Adoption differed by livelihood system rather than following a uniform pattern.</p></list-item>
<list-item><p>Adoption of animal manure was higher among pastoralists due to greater manure availability.</p></list-item>
<list-item><p>Agropastoralists adopted more readily practices that aligned with their prior farming experience.</p></list-item>
<list-item><p>Willingness to continue with at least one practice beyond the trial period was high across all the livelihood systems.</p></list-item>
</list>
<table-wrap position="float" id="T3">
<label>Table 3</label>
<caption><p>Adoption of selected agroecological practices by livelihood system during visit 1.</p></caption>
<table frame="box" rules="all">
<thead>
<tr>
<th valign="top" align="left"><bold>Practice</bold></th>
<th valign="top" align="center"><bold>Kabulokor (Agropastoralists (%) (<italic>n</italic> = 24)</bold></th>
<th valign="top" align="center"><bold>Atala Kamusio (Pastoralists) (%) (<italic>n</italic> = 25)</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Animal manure</td>
<td valign="top" align="center">45%</td>
<td valign="top" align="center">65%</td>
</tr>
<tr>
<td valign="top" align="left">Intercropping</td>
<td valign="top" align="center">50%</td>
<td valign="top" align="center">40%</td>
</tr>
<tr>
<td valign="top" align="left">Pest management by ash</td>
<td valign="top" align="center">35%</td>
<td valign="top" align="center">50%</td>
</tr>
<tr>
<td valign="top" align="left">Mulching</td>
<td valign="top" align="center">25%</td>
<td valign="top" align="center">20%</td>
</tr>
<tr>
<td valign="top" align="left">Bottle irrigation</td>
<td valign="top" align="center">1%</td>
<td valign="top" align="center">1%</td>
</tr>
<tr>
<td valign="top" align="left">Trees planting</td>
<td valign="top" align="center">15%</td>
<td valign="top" align="center">10%</td>
</tr></tbody>
</table>
</table-wrap>
<p>The TIPs results indicate that adoption was shaped primarily by resource availability and existing farming experience by the locals, rather than by differences in openness or willingness to embrace agroecological practices.</p>
</sec>
<sec>
<label>4.3.2</label>
<title>Farmer retention in agroecological practice adoption during TIPs</title>
<p>Beyond initial adoption (first TIPs visit), the retention of agroecological practices over time (second and third TIPs visits) provided insight into their practical feasibility under real-world conditions. <xref ref-type="fig" rid="F5">Figure 5</xref> clearly shows farmer retention across successive TIP visits in the two livelihood systems, capturing the discontinuation of practices due to contextual challenges rather than lack of initial interest.</p>
<fig position="float" id="F5">
<label>Figure 5</label>
<caption><p>Farmer retention in agroecological practice adoption during TIPs.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fsufs-10-1736719-g0005.tif">
<alt-text content-type="machine-generated">Bar chart comparing adoption rates for seven agricultural practices over three visits. Animal manure application, intercropping, and pest control by ash have the highest initial adoption, all declining in subsequent visits. Practices like tree planting and bottle irrigation remain low across all visits. Blue bars represent the first visit, orange the second, and gray the third. Percentages are labeled atop each bar, ranging from fifty-nine percent for animal manure application in the first visit to two percent for bottle irrigation in the first visit. Data measures short-term changes in practice adoption over time.</alt-text>
</graphic>
</fig>
<p>Although initial participation was high during the first visit, retention declined gradually across visits. Drop-outs were largely linked to water shortages, destruction by free roaming animals, and also competing livelihood demands, rather than rejection of the practices themselves. Practices that relied on locally available resources and required relatively little labor showed higher retention rates, thereby indicating greater short-term feasibility of the practices.</p>
<p>While adoption rates differed between agropastoralists and pastoralists systems, the retention trend across visits was similar, suggesting that structural constraints rather than livelihood type alone influenced continued technique use.</p>
</sec>
</sec>
<sec>
<label>4.4</label>
<title>Farmer perceptions of trial plot performance and willingness to continue agroecological practices</title>
<p>Farmers&#x00027; perceptions of trial plot performance and their willingness to continue using agroecological practices were assessed during the final TIP visit (third TIPs visit). The qualitative analysis identified indicators provide insight into perceived effectiveness and short-term sustainability of the tested practices. Overall, farmers&#x00027; assessments of plot performance closely aligned with their stated intentions to continue adopting selected practices beyond the trial period (<xref ref-type="table" rid="T4">Table 4</xref>).</p>
<table-wrap position="float" id="T4">
<label>Table 4</label>
<caption><p>Farmers&#x00027; perceptions of trial plot performance and willingness to continue agroecological practices (<italic>n</italic> = 38).</p></caption>
<table frame="box" rules="all">
<thead>
<tr>
<th valign="top" align="left"><bold>Indicator</bold></th>
<th valign="top" align="left"><bold>Response category</bold></th>
<th valign="top" align="center"><bold>Percentage (%)</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" rowspan="3">Perceived plot performance</td>
<td valign="top" align="left">Trial plots performed better</td>
<td valign="top" align="center">79%</td>
</tr>
<tr>
<td valign="top" align="left">Control plots performed better</td>
<td valign="top" align="center">16%</td>
</tr>
<tr>
<td valign="top" align="left">No noticeable difference</td>
<td valign="top" align="center">5%</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="3">Willingness to continue &#x02265;1 practice</td>
<td valign="top" align="left">willing</td>
<td valign="top" align="center">79%</td>
</tr>
<tr>
<td valign="top" align="left">undecided</td>
<td valign="top" align="center">18%</td>
</tr>
<tr>
<td valign="top" align="left">unwilling</td>
<td valign="top" align="center">3%</td>
</tr></tbody>
</table>
</table-wrap>
<p>It should be noted that although most farmers set up control plots next to their trial plots, a proportion did not do so consistently due to challenges related to land availability, labor, water availability or other resources. The, comparisons between trial and control plots are based on farmer-reported assessments and participatory evaluation during the final workshop rather than standardized experimental measurements.</p>
<p>The majority of farmers (79 %) reported that trial plots performed better than adjacent control plots. They cited improved retention of the moisture in the soil, healthier crop appearance, and reduced crop stress as indicators of better performance. In contrast, 16% of the farmers felt that the control plots performed better and attributed this to the fact there were less pests, and their familiarity with traditional farming practices. Only 5% of the farmers felt that there was no observable difference between the trial plots and control plots.</p>
<disp-quote><p>&#x0201C;<italic>The soil in the trial plot held water longer, and the crops did not dry out as fast as in the control plot.&#x0201D; (Farmer 02, Kabulokor)</italic></p></disp-quote>
<p>These perceptions translated into a high level of willingness to continue with the practices. During the third visit (final visit), 79% of farmers expressed a clear intention to continue using at least one agroecological technique beyond the trial period. A further 18% were undecided, mainly due to uncertainty around input availability, while only 3% reported unwillingness to continue any of the tried practices.</p>
<p>The approaches that utilized local resources, such as ash and animal manure showed the greatest connection with the willingness to continue practicing. On the other hand, practices that required the development particular skills, like bottle irrigation technique, were less likely to be sustained in both systems and showed the need for specific trainings and/or manuals.</p>
<disp-quote><p>&#x0201C;<italic>I will continue using animal manure and ash because they worked well, and I can get them at home.&#x0201D;</italic></p>
<p>&#x0201C;<italic>I would wish to continue using bottle irrigation, but I don&#x00027;t have bottles to use.&#x0201D; [Two farmers in Atala Kamusio]</italic></p></disp-quote>
<list list-type="bullet">
<list-item><p>Perceived improvement in performance in trial plots was linked to farmers&#x00027; willingness to continue using agroecological techniques.</p></list-item>
<list-item><p>Adoption decisions favored techniques that were low-cost, familiar, and based on locally accessible resources like animal manure and ash.</p></list-item>
<list-item><p>Limited resources availability, rather than perceived ineffectiveness, was the primary cause of hesitation or discontinuation of several practices.</p></list-item>
</list>
</sec>
<sec>
<label>4.5</label>
<title>Triangulation of findings</title>
<p><xref ref-type="table" rid="T5">Table 5</xref> summarizes the extent to which key themes identified in FGDs, TIPs, and reflection workshops converged, strengthened, or complemented one another, highlighting the most robust and analytically relevant findings across methods.</p>
<table-wrap position="float" id="T5">
<label>Table 5</label>
<caption><p>Triangulation of key findings across FGDs, Trials of Improved Practices (TIPs), and reflection workshops.</p></caption>
<table frame="box" rules="all">
<thead>
<tr>
<th valign="top" align="left"><bold>Theme</bold></th>
<th valign="top" align="left"><bold>FGDs</bold></th>
<th valign="top" align="left"><bold>TIPs</bold></th>
<th valign="top" align="left"><bold>Workshops</bold></th>
<th valign="top" align="left"><bold>Interpretation type</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Water scarcity</td>
<td valign="top" align="left">Identified as a major production challenge</td>
<td valign="top" align="left">Limited adoption of water-dependent techniques</td>
<td valign="top" align="left">Consistently cited as a barrier to continued use</td>
<td valign="top" align="left">Converged</td>
</tr>
<tr>
<td valign="top" align="left">Pest pressure</td>
<td valign="top" align="left">Widely reported as a key agronomic challenge</td>
<td valign="top" align="left">Ash-based pest management implemented</td>
<td valign="top" align="left">Ash perceived as effective and accessible</td>
<td valign="top" align="left">Converged</td>
</tr>
<tr>
<td valign="top" align="left">Animal manure</td>
<td valign="top" align="left">Frequently proposed as a soil fertility option</td>
<td valign="top" align="left">Most consistently adopted technique</td>
<td valign="top" align="left">Most commonly cited practice farmers intend to continue</td>
<td valign="top" align="left">Converged</td>
</tr>
<tr>
<td valign="top" align="left">Bottle irrigation</td>
<td valign="top" align="left">Initially perceived as a promising solution</td>
<td valign="top" align="left">Very low uptake during trials</td>
<td valign="top" align="left">Practical challenges (technical setup, material availability) identified</td>
<td valign="top" align="left">Strengthened</td>
</tr>
<tr>
<td valign="top" align="left">Crop destruction by livestock</td>
<td valign="top" align="left">Reported as a challenge in some communities</td>
<td valign="top" align="left">Not observed during trial period</td>
<td valign="top" align="left">Re-emphasized as a structural issue requiring fencing</td>
<td valign="top" align="left">Strengthened</td>
</tr>
<tr>
<td valign="top" align="left">Labor and time constraints</td>
<td valign="top" align="left">Not emphasized</td>
<td valign="top" align="left">Emerged during implementation</td>
<td valign="top" align="left">Confirmed as limiting factor for labor-intensive practices</td>
<td valign="top" align="left">Complementary</td>
</tr>
<tr>
<td valign="top" align="left">Peer learning</td>
<td valign="top" align="left">Not discussed</td>
<td valign="top" align="left">Not captured</td>
<td valign="top" align="left">Farmers reported learning from neighboring plots</td>
<td valign="top" align="left">Complementary</td>
</tr></tbody>
</table>
</table-wrap>
<p>Overall, triangulation revealed strong convergence for water scarcity, pest management, and animal manure use, confirming these as central determinants of agroecological adoption. In contrast, practices such as bottle irrigation were initially perceived as promising but were later constrained by practical and technical barriers, illustrating how implementation-based methods strengthened earlier qualitative findings. Complementary insights from reflection workshops further highlighted the role of labor constraints and peer learning in shaping adoption trajectories.</p>
<p>Together, these triangulated findings illustrate how perceived challenges, practical feasibility, and social learning interact to shape short-term agroecological adoption in semi-arid and pastoralist contexts.</p>
</sec>
</sec>
<sec sec-type="discussion" id="s5">
<label>5</label>
<title>Discussion</title>
<sec>
<label>5.1</label>
<title>Interpretation of major findings</title>
<p>This study identifies several interconnected factors shaping vegetable production and agroecological adoption in semi-arid Turkana. These include agronomic and ecological constraints, access to resources, livelihood strategies, and social processes influencing farmer decision-making. Together, these factors explain why some practices were adopted and sustained, while others were discontinued.</p>
<sec>
<label>5.1.1</label>
<title>Major challenges for vegetable production in semi-arid areas and adopted agroecological solutions</title>
<p>Pest infestation emerged as the most critical agronomic challenge. High temperatures and dry conditions likely increased pest pressure and reduced plant resistance, a pattern reported in other dryland systems (<xref ref-type="bibr" rid="B7">Kashyap et al., 2023</xref>). In response, farmers adopted ash-based pest management, a low-cost and locally available practice. Its uptake demonstrates how traditional knowledge can align with agroecological principles to address context-specific challenges.</p>
<p>Water scarcity was another key constraint affecting both crop choice and practice adoption. Farmers tried mulching and bottle irrigation as water-saving options. While mulching was relatively easy to apply, bottle irrigation faced practical limitations, including lack of materials, technical difficulties, and high labor demands. As a result, practices that were technically effective were not sustained when they did not fit local resource conditions.</p>
<p>Poor soil fertility and limited access to quality seeds further constrained vegetables performance. Farmers who applied animal manure reported improved crop vigor and soil condition, highlighting the importance of organic inputs for restoring degraded soils and supporting low-input production systems.</p>
</sec>
<sec>
<label>5.1.2</label>
<title>Influences on the adoption of agroecological practices</title>
<p>Next to the already mentioned challenges when applying bottle irrigation, further socio-economic factors also shaped adoption outcomes. Crop destruction by free-roaming livestock discouraged investment in vegetable production, particularly in pastoral settings. Pastoral mobility further influenced adoption by limiting the time and labor available for plot management. Farmers who moved frequently with livestock were less able to maintain practices requiring regular monitoring or protection, which helps explain lower uptake of labor-intensive techniques.</p>
<p>Knowledge and behavioral factors played an important role as well. Farmers often relied on peer observation to assess whether a practice was worth adopting. Agronomic extension service was not readily available especially for the pastoralist community who asked in the final workshop for training opportunities and learning material which is contextualized to their livelihood. Social learning reduced perceived risk in contexts of high uncertainty and limited extension support. At the same time, risk aversion encouraged preference for practices requiring minimal financial or labor investment. These findings suggest that adoption in drylands is driven as much by livelihood security and flexibility as by short-term productivity gains. Anecdotal evidence from the workshop showed a willingness to support the communities through agriculture extension services. However, the resources to reach the respective pastoralists and agropastoral regularly are limited.</p>
</sec>
<sec>
<label>5.1.3</label>
<title>Importance of continued data collection and exchange with farmers</title>
<p>In general, triangulation of data from the different participatory surveys and discussion rounds showed that some important information such as peer learning only was mentioned during the final workshop. This suggests that farmers may not always share or recognize certain experiences in early stages, but become more open and reflective as trust builds and discussions deepen over time. As a result a mixed-method approach and continued data collection over time is necessary to obtain a holistic understanding of the situation which is the basis for any transition in food systems. Similar patterns have also been reported in participatory and qualitative research, where ongoing and iterative engagement with participants through multiple rounds of data collection helps reveal insights that may not emerge at first, especially those that are hidden, taken for granted, or become clearer only after trust and familiarity are established (<xref ref-type="bibr" rid="B17">Reed et al., 2018</xref>; <xref ref-type="bibr" rid="B5">Jagosh et al., 2012</xref>).</p>
</sec>
</sec>
<sec>
<label>5.2</label>
<title>Theoretical implications</title>
<p>Looking at the results through the Sustainable Livelihoods Framework (SLF) helps to understand why farmers adopt some agroecological practices and not others. Adoption depends not only on how well a practice works, but also on what resources farmers have, the time and labor they can invest, their knowledge and skills, and the support from their community. Practices using resources readily available at home, like animal manure or ash for pest control, were adopted more easily. In contrast, practices that needed extra materials, technical know-how, or more effort&#x02014;like bottle irrigation&#x02014;were harder to maintain.</p>
<p>Social connections and learning from other farmers played an important role, showing the value of social capital. Farmers were more likely to try and continue practices they could observe working successfully on neighboring plots. Differences between agropastoralists and pastoralists show that household resources and livelihood strategies shape which practices are feasible.</p>
<p>Using the framework makes it clear that adoption is influenced by a combination of resources, labor, skills, and social support&#x02014;not just the technical performance of a technique. This perspective helps explain why some practices lasted while others dropped off and highlights how farmers make decisions to manage risk and sustain their livelihoods in challenging, semi-arid conditions.</p>
</sec>
<sec>
<label>5.3</label>
<title>Practical and policy implications</title>
<p>The findings of this study suggest several practical and policy actions that can support sustainable vegetable production in semi-arid drylands:</p>
<list list-type="bullet">
<list-item><p>Prioritize low-cost, locally available inputs, such as animal manure and ash, to enhance soil fertility and pest management.</p></list-item>
<list-item><p>Strengthen farmers&#x00027; technical capacity in practices requiring precision, including water-saving techniques and soil management.</p></list-item>
<list-item><p>Promote peer learning and participatory approaches, including farmer field schools, demonstration plots, and create an environment for farmers owned agronomic trials, to facilitate knowledge sharing and adoption.</p></list-item>
<list-item><p>Tailor interventions to local livelihood systems, considering differences between agropastoralists and pastoralists households.</p></list-item>
<list-item><p>Improve access to quality seeds, protect crops from livestock, and provide essential infrastructure such as water points and fencing.</p></list-item>
<list-item><p>Support local institutions and value chains to ensure sustainability and long-term adoption of agroecological practices.</p></list-item>
<list-item><p>Encourage scaling of effective practices by integrating technical support with social and resource considerations to enhance adoption and resilience.</p></list-item>
</list>
<p>Overall, integrating low-cost, context-specific agroecological practices with technical, social, and institutional support can enhance productivity, household food security, and resilience, providing a foundation for broader scaling and policy adoption.</p>
</sec>
<sec>
<label>5.4</label>
<title>Strengths and limitations</title>
<p>This study relied on short-term Trials of Improved Practices (TIPs), descriptive statistics, and farmers&#x00027; own observation rather than long-term yield monitoring, economic cost&#x02013;benefit analysis, or multi-season performance indicators. The findings should thus not be interpreted as evidence that the agroecological practices are superior or that they will always lead to sustained productivity gains. Instead, the results show what is considered feasible by the agro-pastoralists and pastoralists to implement in their settings indicating that standard agricultural extension service may not be effective. The strength of this study is that it shows how farmers perceive the benefits, and the short-term patterns of adoption under real-world dryland conditions which provides them with limited amount of vegetable which they may not access otherwise (<xref ref-type="bibr" rid="B6">Jordan et al., 2022</xref>; <xref ref-type="bibr" rid="B15">Oduor, 2022</xref>; <xref ref-type="bibr" rid="B16">Oduor et al., 2023</xref>). This approach naturally limits how far the results can be generalized to other areas with different social, ecological, or resource conditions.</p>
<p>Although farmers were encouraged to set up control plots alongside their trial plots, not everyone was able to do so consistently due to the harsh environmental conditions like very low water availability. This made formal experimental comparisons difficult, so we relied on farmers&#x00027; own observations and participatory assessments rather than statistically controlled measurements. The focus of the study was therefore on transparency and farmer-led evaluation to strengthen the self-help capacity rather than experimental precision as the access to the agriculture extension system is limited.</p>
<p>Finally, the adoption patterns we observed are shaped by context-specific factors such as livelihood type, labor availability, mobility, and access to local resources. While these factors are key to understanding adoption in semi-arid drylands, they also mean that the findings should be applied cautiously to other settings. Future research could build on these results by conducting longer-term trials that include farmer led quantitative yield measurements, economic assessments, and gender-focused analyses of labor and decision-making. This would provide stronger evidence of both effectiveness of agroecological practices, the generalizability of the results and the potential for scaling up these practices.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="s6">
<label>6</label>
<title>Conclusion</title>
<p>This study demonstrates that participatory approaches, particularly Trials of Improved Practices (TIPs), offer a robust and context-sensitive method for evaluating agroecological practices in semi-arid drylands. By combining farmer perspectives, on-farm experimentation, and reflection workshops, the study captured not only the agronomic and ecological constraints of vegetable production&#x02014;such as pest pressure, water scarcity, poor soil fertility, and limited seed access&#x02014;but also the social and behavioral factors influencing adoption. Farmers&#x00027; perceptions of trial plot performance closely aligned with their willingness to continue using selected techniques, highlighting that practical feasibility and reliance on locally available, low-cost inputs are key drivers of adoption.</p>
<p>The findings reveal that adoption patterns differ between livelihood systems: pastoralists more readily utilized practices supported by abundant local resources, while agropastoralists favored methods aligned with prior farming experience. Techniques such as animal manure, ash for pest management, and intercropping showed high retention and perceived effectiveness, whereas interventions requiring specialized materials or technical skills, like bottle irrigation, were less sustainable. These patterns indicate that farmer decision-making in resource-limited drylands is shaped by a combination of resource availability, labor constraints, and social learning, rather than technical performance alone.</p>
<p>Overall, this study contributes to agroecological research by showing how participatory trials, local livelihood strategies, and contextual constraints interact to shape how farmers adopt new practices in dryland systems. While the findings are specific to Turkana County, they offer lessons that can be applied in other semi-arid and pastoralist areas. In particular, the study highlights the importance of farmer-led evaluation, the benefits of using low-cost, locally available inputs, and the need to design interventions that fit with farmers&#x00027; everyday realities and resource constraints.</p>
<p>Taken together, these findings offer both methodological and practical insights. Methodologically, they demonstrate the value of TIPs for capturing farmer perspectives, testing feasibility, and understanding adoption dynamics. Practically, they provide guidance for designing agroecological practices that are realistic, scalable, and responsive to the challenges and opportunities of semi-arid environments.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s7">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="SM1">Supplementary material</xref>, further inquiries can be directed to the corresponding author/s.</p>
</sec>
<sec sec-type="ethics-statement" id="s8">
<title>Ethics statement</title>
<p>The studies involving humans were approved by School of Graduate Studies, Turkana University College, Kenya; Institutional Review Board (IRB) of the Alliance of Bioversity International and CIAT (IRB51); and the National Commission for Science, Technology and Innovation (NACOSTI), Kenya (License No. NACOSTI/P/23/29342). The studies were conducted in accordance with the local legislation and institutional requirements. Written informed consent for participation in this study was provided by the participants&#x00027; legal guardians/next of kin.</p>
</sec>
<sec sec-type="author-contributions" id="s9">
<title>Author contributions</title>
<p>AA: Conceptualization, Formal analysis, Writing &#x02013; original draft, Methodology. AW: Formal analysis, Writing &#x02013; review &#x00026; editing, Supervision, Methodology. IJ: Writing &#x02013; review &#x00026; editing, Conceptualization, Resources, Supervision, Project administration, Methodology. GK: Methodology, Data curation, Supervision, Investigation, Resources, Funding acquisition, Writing &#x02013; review &#x00026; editing, Conceptualization, Project administration.</p>
</sec>
<ack><title>Acknowledgments</title><p>We extend our sincere gratitude to the participating communities of Turkana County for their cooperation and valuable insights throughout the study. We also acknowledge the field research team for their dedicated support during data collection. Special appreciation is extended to the supervisors of the first author, Prof. Dr. Peter Edome Akwee and Dr. Godfrey Nakitare Nambafu for their guidance and constructive input during the development of this research. And many thanks to Rebecca Horvath for creating the map showing the study locations.</p>
</ack>
<sec sec-type="COI-statement" id="conf1">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="ai-statement" id="s11">
<title>Generative AI statement</title>
<p>The author(s) declared that generative AI was used in the creation of this manuscript. The author(s) confirm full responsibility for the content of this manuscript. Generative AI tools were used in a limited manner to support language editing, improve clarity, and enhance readability of the text. No generative AI tools were used to generate original research data, analyses, results, or scientific interpretations. All ideas, analyses, and conclusions presented in the manuscript are those of the author(s).</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec sec-type="disclaimer" id="s12">
<title>Publisher&#x00027;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec sec-type="supplementary-material" id="s13">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fsufs.2026.1736719/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fsufs.2026.1736719/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Table_1.DOCX" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/></sec>
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<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3309618/overview">Julian Fernando Becerra Encinales</ext-link>, Cenipalma, Colombia</p>
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