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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Agron.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Agronomy</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Agron.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">2673-3218</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fagro.2026.1748080</article-id>
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<article-categories>
<subj-group subj-group-type="heading">
<subject>Systematic Review</subject>
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</article-categories>
<title-group>
<article-title>Greenhouse gas emissions in maize agroecosystems of Sub-Saharan Africa: evidence synthesis and mitigation insights</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Mussa</surname><given-names>Chisomo J.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>*</sup></xref>
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<contrib contrib-type="author">
<name><surname>Ololade</surname><given-names>Olusola O.</given-names></name>
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<name><surname>Lark</surname><given-names>R. Murray</given-names></name>
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<name><surname>Dlamini</surname><given-names>Jerry C.</given-names></name>
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<name><surname>Nalivata</surname><given-names>Patson C.</given-names></name>
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<name><surname>Chimungu</surname><given-names>Joseph</given-names></name>
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<name><surname>Louro-L&#xf3;pez</surname><given-names>Ar&#xe1;nzazu</given-names></name>
<xref ref-type="aff" rid="aff5"><sup>5</sup></xref>
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<contrib contrib-type="author">
<name><surname>Cardenas</surname><given-names>Laura M.</given-names></name>
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<aff id="aff1"><label>1</label><institution>Centre for Environmental Management, University of the Free State</institution>, <city>Bloemfontein</city>,&#xa0;<country country="za">South Africa</country></aff>
<aff id="aff2"><label>2</label><institution>Lilongwe University of Agriculture and Natural Resources</institution>, <city>Lilongwe</city>,&#xa0;<country country="mw">Malawi</country></aff>
<aff id="aff3"><label>3</label><institution>University of Nottingham</institution>, <city>Nottingham</city>,&#xa0;<country country="gb">United Kingdom</country></aff>
<aff id="aff4"><label>4</label><institution>Unit for Environmental Sciences and Management, North-West University</institution>, <city>Potchefstroom</city>,&#xa0;<country country="za">South Africa</country></aff>
<aff id="aff5"><label>5</label><institution>Net Zero and Resilient Farming, Rothamsted Research</institution>, <city>Harpenden</city>,&#xa0;<country country="gb">United Kingdom</country></aff>
<author-notes>
<corresp id="c001"><label>*</label>Correspondence: Chisomo J. Mussa, <email xlink:href="mailto:mussachisomo@gmail.com">mussachisomo@gmail.com</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-02-11">
<day>11</day>
<month>02</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>8</volume>
<elocation-id>1748080</elocation-id>
<history>
<date date-type="received">
<day>20</day>
<month>11</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>19</day>
<month>01</month>
<year>2026</year>
</date>
<date date-type="rev-recd">
<day>17</day>
<month>01</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Mussa, Ololade, Lark, Dlamini, Nalivata, Chimungu, Louro-L&#xf3;pez and Cardenas.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Mussa, Ololade, Lark, Dlamini, Nalivata, Chimungu, Louro-L&#xf3;pez and Cardenas</copyright-holder>
<license>
<ali:license_ref start_date="2026-02-11">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>
<p>Maize-based agroecosystems dominate food production across much of Sub-Saharan Africa (SSA) and are central to regional food security. At the same time, agricultural soils are important sources of greenhouse gas (GHG) emissions, particularly nitrous oxide (N<sub>2</sub>O), carbon dioxide (CO<sub>2</sub>) and methane (CH<sub>4</sub>), raising concerns about the climate impacts of maize intensification. Although a broad body of agronomic research in SSA has examined soil carbon dynamics, nitrogen cycling and productivity trade-offs, evidence based on field-measured GHG fluxes from maize systems remains limited. This review synthesises experimental, field-based studies that quantify CO<sub>2</sub>, N<sub>2</sub>O and CH<sub>4</sub> emissions from maize agroecosystems in SSA to characterise emission levels, identify key emission drivers and assess the mitigation potential of various management strategies. A PRISMA-guided systematic mapping and narrative synthesis was conducted using Web of Science and Scopus databases. Twenty-one field-based studies met the inclusion criteria and were analysed using bibliometric and thematic approaches. Across the reviewed studies, GHG emissions from maize systems in SSA were generally lower than those reported from high-input systems elsewhere, attributed to low nitrogen inputs and prevailing environmental conditions. Nitrogen management and soil moisture consistently emerged as dominant controls of N<sub>2</sub>O emissions, which typically contributed most to overall global warming potential. Carbon dioxide fluxes were strongly influenced by tillage practices and residue management, while soils commonly acted as net sinks for CH<sub>4</sub>, with episodic emissions during prolonged wet conditions. Evidence on conservation agriculture components points to context-dependent mitigation potential, with trade-offs among CO<sub>2</sub>, N<sub>2</sub>O and CH<sub>4</sub> varying by soil type, climate and management intensity. The review highlights the need for long-term, multi-site field experiments, particularly in underrepresented regions, to support the development of context-specific, climate-smart maize production strategies in SSA.</p>
</abstract>
<kwd-group>
<kwd>conservation agriculture</kwd>
<kwd>conventional tillage</kwd>
<kwd>greenhouse gas emissions</kwd>
<kwd>maize</kwd>
<kwd>nitrous oxide</kwd>
<kwd>Sub-Saharan Africa</kwd>
<kwd>yield-scaled emissions</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This review was part of a funded project under the European Joint Programme (EJP) on Soils, &#x201c;The effect of conservation agriculture interventions on greenhouse gas emissions&#x201d; grant number EJP SOIL/I/108/CropGas/2022 and was co-funded by the UK Biotechnology and Biological Sciences Research Council (UKRI-BBSRC) under award BB/X002993/1 (2022&#x2013;2024) and the Global Research Alliance. Rothamsted authors acknowledge contributions from the Growing Health (BB/X010953/1) and the Resilient Farming Futures (BB/X010961/1) Institute Strategic Programs.</funding-statement>
</funding-group>
<counts>
<fig-count count="5"/>
<table-count count="2"/>
<equation-count count="0"/>
<ref-count count="59"/>
<page-count count="14"/>
<word-count count="6792"/>
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<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Climate-Smart Agronomy</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Agriculture is a major contributor to global GHG emissions, with cropland soils representing a dominant source of N<sub>2</sub>O and an important regulator of CO<sub>2</sub> and CH<sub>4</sub> fluxes (<xref ref-type="bibr" rid="B5">Brouziyne et&#xa0;al., 2023</xref>). In SSA, maize (Zea mays L.) is the most widely cultivated staple crop and central to food security and rural livelihoods for a large proportion of the population (<xref ref-type="bibr" rid="B53">ten Berge et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B10">Erenstein et&#xa0;al., 2022</xref>). Maize production in the region is dominated by smallholder systems characterised by low external inputs, high climate variability, and strong dependence on soil fertility and rainfall (<xref ref-type="bibr" rid="B28">Macharia et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B36">Musafiri et&#xa0;al., 2020b</xref>; <xref ref-type="bibr" rid="B12">Githongo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B51">Tabe-Ojong, 2023</xref>). As population growth and food demand intensify, improving maize productivity while limiting environmental externalities&#x2014;particularly GHG emissions&#x2014;has become a central challenge for sustainable maize intensification in SSA.</p>
<p>Empirical research explicitly quantifying GHG emissions from maize-based systems in SSA has expanded over the past two decades, particularly in East and Southern Africa. Field-based studies from countries such as Kenya, Tanzania, Ethiopia, South Africa, and Zimbabwe have measured CO<sub>2</sub>, N<sub>2</sub>O, and CH<sub>4</sub> fluxes under a range of management practices, including varying nitrogen (N) input levels, tillage intensity, residue management, crop rotation, and intercropping. Beyond studies that directly measure GHG fluxes, a much broader body of research across SSA has examined processes and outcomes that are closely linked to emissions and mitigation potential in maize-based systems. These include investigations of soil organic carbon sequestration (<xref ref-type="bibr" rid="B31">McNair Bostick et&#xa0;al., 2007</xref>; <xref ref-type="bibr" rid="B13">Gram et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B50">Sundberg et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B1">Abdalla et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B57">Zheng et&#xa0;al., 2023</xref>), nitrogen budgets and loss pathways (<xref ref-type="bibr" rid="B7">Chikowo et&#xa0;al., 2006</xref>; <xref ref-type="bibr" rid="B13">Gram et&#xa0;al., 2020</xref>), fertiliser response curves (<xref ref-type="bibr" rid="B25">Lemarpe et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B29">Maertens et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B57">Zheng et&#xa0;al., 2023</xref>), yield gaps (<xref ref-type="bibr" rid="B4">Bellarby et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B46">Rusere et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B29">Maertens et&#xa0;al., 2023</xref>), and trade-offs associated with agricultural intensification (<xref ref-type="bibr" rid="B4">Bellarby et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B57">Zheng et&#xa0;al., 2023</xref>). Numerous studies have assessed integrated soil fertility management, organic and inorganic nutrient inputs, agroforestry systems, improved fallows, and climate-smart agricultural practices, often using modelling approaches and other process-based frameworks (<xref ref-type="bibr" rid="B9">Ellis-Jones and Tengberg, 2000</xref>; <xref ref-type="bibr" rid="B42">Pyle and Mirza, 2007</xref>; <xref ref-type="bibr" rid="B45">Roobroeck et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B27">Macharia et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B46">Rusere et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B59">Zizinga et&#xa0;al., 2022</xref>). While many of these studies do not report field-measured GHG emissions from maize plots, they provide critical indirect insights into the biophysical mechanisms controlling emissions, including nitrogen availability, carbon inputs, soil aeration, and water dynamics.</p>
<p>Conservation agriculture (CA), based on the principles of minimal soil disturbance, permanent soil cover, and crop diversification, has been widely promoted in SSA as a climate-smart approach to enhance productivity, resilience, and environmental sustainability (<xref ref-type="bibr" rid="B21">Kimaro et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B19">Kimaro et&#xa0;al., 2016a</xref>; <xref ref-type="bibr" rid="B23">Kulagowski et&#xa0;al., 2021</xref>). Evidence from SSA and other regions suggests that CA practices can increase soil organic carbon stocks and reduce CO<sub>2</sub> emissions, while their effects on N<sub>2</sub>O and CH<sub>4</sub> are more variable and strongly context dependent (<xref ref-type="bibr" rid="B48">Soler et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B20">Kimaro et&#xa0;al., 2016b</xref>; <xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>). In SSA, several studies have evaluated individual CA components&#x2014;such as reduced tillage (<xref ref-type="bibr" rid="B6">Centre and Centre, 2008</xref>; <xref ref-type="bibr" rid="B16">Hickman et&#xa0;al., 2015a</xref>; <xref ref-type="bibr" rid="B54">Tongwane et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B56">Vilakazi et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B55">Tully et&#xa0;al., 2023</xref>), residue retention, and legume integration (<xref ref-type="bibr" rid="B32">Millar et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B38">Nyamadzawo et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B33">Mirzaei et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B55">Tully et&#xa0;al., 2023</xref>)&#x2014;and have reported mixed effects on GHG emissions, contingent on factors such as soil texture, residue quality, nitrogen inputs and rainfall regime. However, the magnitude and consistency of reported mitigation benefits remain unclear.</p>
<p>This review examines the existing literature on GHG emissions from maize agroecosystems in SSA and evaluates the impact of various mitigation strategies on these emissions. By identifying research gaps and synthesising current knowledge, the review aims to provide an understanding of current emissions levels, influencing factors, and insights into the mitigation strategies implemented in the region. A comprehensive understanding of the interactions among maize production, mitigation practices, and GHG dynamics will support the development of sustainable agricultural systems in SSA and help address the interconnected challenges of food security and environmental sustainability.</p>
</sec>
<sec id="s2">
<label>2</label>
<title>Methodology</title>
<p>This study followed PRISMA guidelines to conduct a systematic review of GHG emissions from maize agroecosystems in SSA. The review focussed specifically on experimental, field-based studies that directly quantified soil&#x2013;atmosphere fluxes of CO<sub>2</sub>, N<sub>2</sub>O, and/or CH<sub>4</sub> from maize production systems. This narrow scope was adopted to ensure comparability of emission estimates and to synthesise evidence derived from direct measurements, while recognising that a broader body of agronomic and modelling literature relevant to mitigation processes exists outside these criteria. The review was guided by three research questions: (i) What are the reported magnitudes of GHG emissions from maize systems in SSA? (ii) What environmental and management factors influence emission dynamics? and (iii) What mitigation strategies have been evaluated, and what trade-offs do they present in terms of emissions and productivity? The review process adapted the methodology outlined by <xref ref-type="bibr" rid="B47">Sharaf-Addin (2024)</xref> (<xref ref-type="fig" rid="f1"><bold>Figure&#xa0;1</bold></xref>). The initial step involved identifying relevant keywords and developing a search strategy to capture studies that effectively address the research questions. The keywords were then refined and combined in various ways to generate the most relevant articles on GHG emissions in maize agroecosystems within the SSA region.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>The literature review process for the study [adapted from <xref ref-type="bibr" rid="B47">Sharaf-Addin (2024)</xref>].</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fagro-08-1748080-g001.tif">
<alt-text content-type="machine-generated">Flowchart depicting a research process with five steps. Step 1: Preliminary study leads to research questions, search keywords, and strategy. Step 2: Formulating research questions determines their quality. Step 3: Screening of publications limits them to inclusion and exclusion criteria. Step 4: Eligibility and quality assessment ensures publications answer the research questions. Step 5: Data extraction and compilation provide comprehensive knowledge from included studies.</alt-text>
</graphic></fig>
<sec id="s2_1">
<label>2.1</label>
<title>Literature search strategy</title>
<p>A literature search was conducted on 22 March 2025 using the Web of Science and Scopus databases. Searches were performed across titles, abstracts, and author keywords and used a structured Boolean strategy with three keyword blocks. The first block captured maize systems using the terms &#x201c;maize&#x201d; OR &#x201c;corn&#x201d; OR &#x201c;Zea mays&#x201d;. The second block captured GHG-related studies using &#x201c;greenhouse gas&#x201d; OR &#x201c;GHG&#x201d; OR &#x201c;emission&#x201d; OR &#x201c;flux*&#x201d; OR &#x201c;nitrous oxide&#x201d; OR &#x201c;N2O&#x201d; OR &#x201c;methane&#x201d; OR &#x201c;CH4&#x201d; OR &#x201c;carbon dioxide&#x201d; OR &#x201c;CO2&#x201d;. The third block restricted retrieval to Sub-Saharan Africa by including regional terms (&#x201c;sub-Saharan Africa&#x201d;, &#x201c;SSA&#x201d;, and East/West/Central/Southern Africa**) and the names of Sub-Saharan African countries (e.g., Malawi, Kenya, Uganda, Tanzania, Zambia, Zimbabwe, Nigeria, Ghana, Ethiopia, South Africa, among others). The three blocks were combined using AND (maize terms AND GHG terms AND SSA terms), while synonymous terms within each block were combined using OR, to ensure that retrieved records contained maize-related terms and at least one GHG/emissions term alongside a Sub-Saharan Africa location term.</p>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Inclusion and exclusion criteria</title>
<p>Records retrieved from the database searches were screened and studies were included if they were peer-reviewed, field-based experiments conducted in Sub-Saharan Africa under maize-based cropping systems and reported quantitative soil&#x2013;atmosphere greenhouse gas fluxes of CO<sub>2</sub>, N<sub>2</sub>O and/or CH<sub>4</sub>. Studies were excluded if they were conducted outside Sub-Saharan Africa, did not involve maize (Zea mays) systems, or did not report quantitative GHG emissions/flux data. We also excluded studies based on laboratory incubations, modelling/simulation, life-cycle assessment, or other indirect estimation approaches without field flux measurements relevant to maize systems. The full inclusion and exclusion criteria are summarised in <xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref>.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Criteria for inclusion and exclusion.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="left">Inclusion criteria</th>
<th valign="middle" align="left">Exclusion criteria</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="left">&#x2022;&#x2003;Study design: Experimental, field-based study (on-farm or research station) in which maize management treatments were applied and compared.</td>
<td valign="middle" align="left">&#x2022;&#x2003;Not field-based: laboratory based (e.g. soil cores), pot trials, or purely observational studies without an experimental field component.</td>
</tr>
<tr>
<td valign="middle" align="left">&#x2022;&#x2003;Geography: Conducted in Sub-Saharan Africa (SSA) (study site located within SSA).</td>
<td valign="middle" align="left">&#x2022;&#x2003;Conducted outside SSA, or location not in SSA.</td>
</tr>
<tr>
<td valign="middle" align="left">&#x2022;&#x2003;Cropping system: Includes maize (Zea mays) as a main crop (sole maize, maize-based rotation, or maize intercrop with maize plot-level results).</td>
<td valign="middle" align="left">&#x2022;&#x2003;Non-maize systems crops only), or maize not separable (no maize plot-level data).</td>
</tr>
<tr>
<td valign="middle" align="left">&#x2022;&#x2003;Outcome: Reports quantitative soil&#x2013;atmosphere GHG fluxes/emissions for at least one gas (CO<sub>2</sub>, N<sub>2</sub>O, and/or CH<sub>4</sub>) measured in the field (Using static chamber method)<break/>&#x2022;&#x2003;Publication type: Peer-reviewed journal article.<break/>&#x2022;&#x2003;Relevance: Addresses GHG emissions from maize systems in relation to management and/or environmental drivers (e.g., N inputs, tillage, residue management, rotations/intercropping).</td>
<td valign="middle" align="left">&#x2022;&#x2003;No quantitative soil&#x2013;atmosphere GHG flux/emission data (e.g., qualitative discussion only, SOC stock change only, yield-only, nutrient balances only, proxy indicators).<break/>&#x2022;&#x2003;Reviews, editorials, conference abstracts, theses/reports (if excluded), and non&#x2013;peer-reviewed sources.<break/>&#x2022;&#x2003;Studies focussed on life cycle assessment/carbon footprint of inputs or supply chains (e.g., fertiliser manufacture, transport, processing) without field flux measurements</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Study screening and selection</title>
<p>The study selection process followed PRISMA 2020 reporting guidelines. All records retrieved from Web of Science and Scopus were exported to Mendeley desktop for reference management and duplicate removal prior to screening. The remaining records were screened in two stages: (i) title and abstract screening to exclude clearly irrelevant studies, followed by (ii) full-text assessment to confirm eligibility against the predefined inclusion and exclusion criteria (<xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref>). During full-text screening, reasons for exclusion were recorded (e.g., conducted outside SSA, non-maize systems, non-field approaches such as modelling or laboratory incubations, or absence of quantitative GHG flux/emission data). The number of records retained at each stage&#x2014;identification, screening, eligibility, and inclusion&#x2014;is summarised in the PRISMA flow diagram (<xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2</bold></xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>PRISMA flowchart for the systematic literature review.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fagro-08-1748080-g002.tif">
<alt-text content-type="machine-generated">Flowchart titled &#x201c;Identification of studies via databases,&#x201d; illustrating the screening process. Initially, 1,989 records were identified from SCOPUS and Web of Science. After removing duplicates, 1,534 records remained. Titles and abstracts of 1,531 records were screened, excluding 1,010 for various reasons. Twenty-eight reports were sought for retrieval; three were not retrieved. Twenty-five full-text reports were assessed, with four excluded. Ultimately, 21 studies were included in the review.</alt-text>
</graphic></fig>
</sec>
<sec id="s2_4">
<label>2.4</label>
<title>Data extraction and synthesis</title>
<p>For each eligible study, data were extracted into a structured spreadsheet using a predefined extraction template. Extracted fields included bibliographic details (authors, year, journal and DOI), study setting (country/region, site description and climate/rainfall regime where reported), experimental design and measurement approach and agronomic management (cropping system, tillage/residue management, crop diversification such as rotations or intercropping, and fertiliser and/or organic amendment inputs including rates and forms). Greenhouse gas outcomes were extracted as reported (CO<sub>2</sub>, N<sub>2</sub>O and/or CH<sub>4</sub> fluxes and, where provided, cumulative or seasonal emissions), together with the units and reporting period. Bibliometric analyses of the retrieved literature were conducted in RStudio using Biblioshiny (bibliometrix) to summarise publication trends, dominant research themes, keyword co-occurrence networks, and the geographical distribution of studies. Findings were synthesised using systematic mapping and narrative synthesis, grouping results by gas type (CO<sub>2</sub>, N<sub>2</sub>O, CH<sub>4</sub>), management category (e.g., nitrogen inputs, tillage intensity, residue retention, crop diversification), and environmental context (e.g., rainfall seasonality, soil moisture status and temperature where reported). Emission responses were interpreted in relation to management-driven mechanisms (particularly nitrogen availability and residue/organic matter inputs) and site conditions known to influence GHG production and transport, with attention to context dependence and trade-offs between mitigation potential and productivity.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results and discussion</title>
<sec id="s3_1">
<label>3.1</label>
<title>Search outcomes and study selection</title>
<p>The literature search identified 1,989 records from Web of Science (n = 1,416) and Scopus (n = 573). After merging records in Mendeley and removing 455 duplicates, 1,531 unique records remained for title and abstract screening. At this stage, 1,503 records were excluded because they did not meet the core scope of the review as defined in <xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref>. The main reasons for exclusion at title/abstract screening were studies conducted outside Sub-Saharan Africa (n = 687), studies that were not maize-based or did not provide maize plot-level outcomes (n = 391), and studies that did not report quantitative soil&#x2013;atmosphere GHG fluxes/emissions (n = 369). A small number of records were excluded because they were life-cycle/carbon footprint assessments without field flux measurements (n = 6) or modelling-only studies without field flux measurements/validation (n = 1). The remaining exclusions (n = 49) comprised other ineligible records evident at title/abstract stage, including non-experimental or non-field-based studies, non-eligible document types, and records that did not meet the inclusion criteria in <xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref> upon closer inspection. Following title/abstract screening, 28 full-text reports were sought for retrieval; three reports could not be retrieved (n = 3). The remaining 25 full texts were assessed for eligibility, and four were excluded because the GHG emissions were reported only as aggregated summaries without extractable plot or treatment level values, however, these studies were still considered qualitatively and cited where relevant in the discussion. In total, 21 studies met all eligibility criteria and were included in the narrative synthesis (<xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2</bold></xref>). All included studies were experimental, field-based investigations conducted in SSA that reported quantitative measurements of at least one greenhouse gas (CO<sub>2</sub>, N<sub>2</sub>O and/or CH<sub>4</sub>) from maize-based cropping systems.</p>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Geographic and thematic distribution of studies</title>
<p>The included studies were unevenly distributed across the Sub-Saharan Africa region (<xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3</bold></xref>). Experimental evidence was concentrated in a limited number of countries, with Kenya accounting for the largest proportion of studies, followed by South Africa and Tanzania. Additional studies were identified from Ethiopia, Zimbabwe, Uganda and Ghana. This geographic clustering reflects the presence of long-term experimental sites and established research infrastructure in these countries. Thematic analysis revealed that most studies focussed on the quantification of N<sub>2</sub>O emissions in relation to nitrogen management, with comparatively fewer investigations explicitly measuring CO<sub>2</sub> and CH<sub>4</sub> fluxes. Key research themes included fertiliser application rates, soil fertility management, tillage intensity, residue management, and crop diversification practices. Several studies also integrated assessments of soil carbon sequestration, yield performance, and global warming potential, highlighting efforts to link emissions with productivity outcomes. The distribution of studies indicates a strong emphasis on nitrogen-driven emission processes in maize systems, while integrated assessments of multiple greenhouse gases and long-term mitigation outcomes remain less common.</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>GHG emissions research output in SSA.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fagro-08-1748080-g003.tif">
<alt-text content-type="machine-generated">Map of Africa showing the number of studies per country. Gray indicates zero studies, purple indicates one study, blue indicates two studies, orange indicates three studies, and green indicates twelve studies. A scale bar indicates distances of zero to two thousand kilometers.</alt-text>
</graphic></fig>
</sec>
<sec id="s3_3">
<label>3.3</label>
<title>Key themes and insights</title>
<p>Further analysis of keyword frequency and co-occurrence reveals how research on GHG emissions from maize systems in SSA has been conceptually framed (<xref ref-type="fig" rid="f4"><bold>Figures&#xa0;4</bold></xref>, <xref ref-type="fig" rid="f5"><bold>5</bold></xref>). The dominant research theme centres on N<sub>2</sub>O emissions associated with nitrogen inputs, highlighting the central role of nitrogen availability and cycling in regulating climate impacts of maize production. This focus reflects broader concerns regarding fertiliser-driven emission increases under intensification scenarios. A second major theme relates to soil and crop management practices, including tillage intensity, residue retention, crop rotation, and intercropping. These practices are frequently linked with soil organic carbon dynamics, microbial activity, and nitrogen use efficiency, highlighting an emerging interest in connecting emission outcomes with soil health and system sustainability. The co-occurrence of terms such as &#x201c;carbon sequestration&#x201d;, &#x201c;crop residues&#x201d;, and &#x201c;crop rotation&#x201d; suggests that mitigation is increasingly being evaluated alongside longer-term soil fertility and resilience considerations. Methane appears as a secondary theme, typically associated with soil moisture conditions and more complex or diversified production systems, such as agroforestry. This reflects the predominantly aerobic conditions of upland maize systems in SSA, where CH<sub>4</sub> emissions are generally low but may become important under specific hydrological conditions (<xref ref-type="bibr" rid="B36">Musafiri et&#xa0;al., 2020b</xref>).</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>A word cloud visualisation of the most frequently used keywords.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fagro-08-1748080-g004.tif">
<alt-text content-type="machine-generated">Word cloud featuring terms related to agriculture and environmental science. Prominent words include &#x201c;Kenya,&#x201d; &#x201c;greenhouse gas,&#x201d; &#x201c;maize,&#x201d; &#x201c;nitrous oxide,&#x201d; &#x201c;carbon dioxide,&#x201d; and &#x201c;fertilizer application.&#x201d; Other words such as &#x201c;soil,&#x201d; &#x201c;Tanzania,&#x201d; &#x201c;forestry,&#x201d; &#x201c;methane,&#x201d; and &#x201c;nitrogen&#x201d; are also present in various colors and sizes.</alt-text>
</graphic></fig>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Co-Occurrence network of Keywords from the reviewed studies.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fagro-08-1748080-g005.tif">
<alt-text content-type="machine-generated">Network diagram depicting relationships between keywords related to agriculture and environmental science. Central terms like &#x201c;Maize,&#x201d; &#x201c;Kenya,&#x201d; &#x201c;Nitrous Oxide,&#x201d; and &#x201c;Zeal Mays&#x201d; are linked to others such as &#x201c;greenhouse gas,&#x201d; &#x201c;fertilizer application,&#x201d; and &#x201c;carbon sequestration.&#x201d; Nodes are colored differently, indicating varied categories or themes.</alt-text>
</graphic></fig>
</sec>
<sec id="s3_4">
<label>3.4</label>
<title>Characteristics of GHG emissions from maize agroecosystems in SSA</title>
<p>Across the reviewed studies, maize-based agroecosystems in SSA exhibited distinct GHG emission characteristics shaped by low external inputs, strong seasonal climatic variability, and site-specific soil properties. Although CO<sub>2</sub>, N<sub>2</sub>O, and CH<sub>4</sub> were all reported, their relative contributions to overall climate impact differed substantially, with N<sub>2</sub>O consistently dominating the global warming potential of maize systems (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>). Carbon dioxide emissions represented the largest absolute fluxes among the measured gases and were closely associated with soil respiration processes (<xref ref-type="bibr" rid="B28">Macharia et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B36">Musafiri et&#xa0;al., 2020b</xref>; <xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>). Across studies, CO<sub>2</sub> fluxes displayed pronounced temporal variability, with emission peaks commonly occurring following rainfall events that stimulated microbial activity and root respiration (<xref ref-type="bibr" rid="B26">Maccarthy et&#xa0;al., 2018</xref>). Tillage intensity and residue management further influenced CO<sub>2</sub> dynamics, with higher emissions generally reported under conventional tillage and residue incorporation compared with reduced or no-tillage systems (<xref ref-type="bibr" rid="B19">Kimaro et&#xa0;al., 2016a</xref>; <xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>). Importantly, several studies reported increases in soil organic carbon under reduced disturbance and residue retention, indicating that short-term CO<sub>2</sub> emission pulses do not necessarily imply long-term carbon losses. Nitrous oxide was the most frequently measured greenhouse gas and emerged as the primary contributor to climate forcing in maize systems across SSA. Emission dynamics were strongly regulated by nitrogen availability and soil moisture, with pronounced N<sub>2</sub>O pulses following fertiliser application and during wetting events after dry periods (<xref ref-type="bibr" rid="B15">Hickman et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B35">Musafiri et&#xa0;al., 2020a</xref>). Across studies, N<sub>2</sub>O responses to increasing nitrogen inputs were often nonlinear, with disproportionately large emission increases observed beyond certain fertiliser thresholds (<xref ref-type="bibr" rid="B14">Hickman et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>). Despite this sensitivity, absolute N<sub>2</sub>O emissions reported in SSA were generally lower than those observed in high-input maize systems elsewhere, reflecting lower fertiliser use and nutrient-limited conditions typical of smallholder production systems (<xref ref-type="bibr" rid="B24">Leitner et&#xa0;al., 2020</xref>). For instance, N<sub>2</sub>O emissions from maize farming systems in Michigan, USA, were found to be ten times higher than those in SSA and in Peru, maize-legume rotations receiving 100 kg N/ha had an emission factor of 1.53%, while a maize chop-and-mulch system in Brazil reported an emission factor of 2.3% (<xref ref-type="bibr" rid="B41">Pauw et&#xa0;al., 2018</xref>). Methane fluxes on the other hand, were assessed less frequently, consistent with the predominantly aerobic conditions of upland maize systems. Where measured, soils commonly functioned as net CH<sub>4</sub> sinks, particularly during dry periods. Episodic CH<sub>4</sub> emissions were observed under prolonged soil saturation, when anaerobic microsites favoured methanogenic activity and reduced CH<sub>4</sub> oxidation (<xref ref-type="bibr" rid="B20">Kimaro et&#xa0;al., 2016b</xref>; <xref ref-type="bibr" rid="B40">Ortiz-Gonzalo et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B28">Macharia et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B35">Musafiri et&#xa0;al., 2020a</xref>; <xref ref-type="bibr" rid="B18">Kibet et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B34">Mosongo et&#xa0;al., 2022</xref>). These findings indicate that CH<sub>4</sub> dynamics in maize systems are highly sensitive to short-term hydrological conditions and may become increasingly variable under changing rainfall regimes.</p>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>GHG emissions studies in SSA.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Publication (Location)</th>
<th valign="middle" align="center">Soil type</th>
<th valign="middle" align="center">Crop management/Treatment</th>
<th valign="middle" align="center">Fertilisation rate (kg N ha<sup>&#x2212;1</sup>)</th>
<th valign="middle" align="center">CO<sub>2</sub> emissions (Mg CO<sub>2</sub>&#x2013;C ha<sup>&#x2212;1</sup>yr<sup>&#x2212;1</sup>)</th>
<th valign="middle" align="center">N<sub>2</sub>O emissions (kg N ha<sup>&#x2212;1</sup> yr<sup>&#x2212;1</sup>)</th>
<th valign="middle" align="center">CH<sub>4</sub> emissions (kg CH<sub>4</sub>&#x2013;C ha<sup>&#x2212;1</sup>yr<sup>&#x2212;1</sup>)</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B17">Hickman et&#xa0;al., 2015b</xref>)<break/>(Ethiopia)</td>
<td valign="middle" align="center">Andosols</td>
<td valign="middle" align="center">No N Control<break/>Fertilised maize monocrop<break/>Crotalaria intercropping at 3 weeks<break/>Crotalaria intercropping at 6 weeks<break/>Lablab intercropping at 3 weeks<break/>Lablab intercropping at 6 weeks</td>
<td valign="middle" align="center">0<break/>64<break/>64<break/>64<break/>64<break/>64</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.10 - 1.20<break/>0.18 - 2.06<break/>0.15 - 3.00<break/>0.18 - 2.12<break/>0.17 - 5.49<break/>0.13 - 0.94</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B26">Maccarthy et&#xa0;al., 2018</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Humic Nitisol</td>
<td valign="middle" align="center">No N Control<break/>Inorganic fertiliser<break/>Animal manure<break/>Animal manure+inorganic fertiliser</td>
<td valign="middle" align="center">0<break/>120<break/>120<break/>60 + 60</td>
<td valign="middle" align="center">4.63 - 4.98<break/>6.33 - 6.82<break/>5.55 - 5.89<break/>5.90 - 6.07</td>
<td valign="middle" align="center">0.20 - 0.22<break/>0.36 - 0.40<break/>0.26 - 0.28<break/>0.30 - 0.32</td>
<td valign="middle" align="center">-2.74 - 2.06<break/>-1.67 - 1.59<break/>-2.26 - -2.10<break/>-1.72 - -1.52</td>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>)<break/>(Iringa and Mbeya, Tanzania)</td>
<td valign="middle" align="center">Haplustalfs</td>
<td valign="middle" align="center">No N Control<break/>Moderate N input<break/>Optimal N input<break/>High N input<break/>Inorganic fertiliser and stover<break/>Inorganic fertiliser and stover</td>
<td valign="middle" align="center">0<break/>50<break/>100<break/>150<break/>50 + Stover 2Mg C ha<sup>&#x2212;1</sup><break/>150 + Stover 2Mg C ha<sup>&#x2212;1</sup></td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.14 - 0.30<break/>0.26 - 0.51<break/>0.30 - 0.58<break/>0.34 - 0.73<break/>0.37 - 0.88<break/>0.55 &#x2013; 2.38</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B52">Tegha et&#xa0;al., 2024</xref>)<break/>(Tanzania)</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">Conventional cultivation<break/>Reduced tillage + surface mulch<break/>Reduced tillage + mulch + legume cover crop<break/>Reduced tillage + mulch + nitrogen fertiliser<break/>Reduced tillage + mulch + woody legumes</td>
<td valign="middle" align="center">100<break/>100<break/>100<break/>100<break/>100</td>
<td valign="middle" align="center">3.92 - 5.74<break/>4.01 - 5.66<break/>4.63 - 6.41<break/>4.47 - 6.04<break/>3.75 - 7.18</td>
<td valign="middle" align="center">0.33 - 0.59<break/>0.32 - 0.54<break/>0.59 - 0.73<break/>0.41 - 0.63<break/>0.49 - 1.22</td>
<td valign="middle" align="center">-2.07 - 3.65<break/>-3.42 - 10.74<break/>0.87 - 7.38<break/>-3.95 - 1.33<break/>-1.52 - 0.16</td>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B18">Kibet et&#xa0;al., 2022</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Ferralsol</td>
<td valign="middle" align="center">Maize monocrop</td>
<td valign="middle" align="center">125</td>
<td valign="middle" align="center">5.95 &#x2013; 7.07</td>
<td valign="middle" align="center">0.93 &#x2013; 1.89</td>
<td valign="middle" align="center">-1.31 - - 0.79</td>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B36">Musafiri et&#xa0;al., 2020b</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Humic Nitisol</td>
<td valign="middle" align="center">No N Control<break/>Tithnia green manure<break/>Inorganic fertiliser</td>
<td valign="middle" align="center">0<break/>60<break/>60</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.64<break/>1.10<break/>0.11</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B8">Chikowo et&#xa0;al., 2007</xref>)<break/>(South Africa)</td>
<td valign="middle" align="center">Haplic Cambisol</td>
<td valign="middle" align="center">No Till<break/>Conventional Tillage<break/>Residues removed<break/>Residues retained<break/>Biochar incorporation<break/>Maize-Fallow-Maize rotation<break/>Maize - Oat - Maize rotation<break/>Maize - Vetch - Maize rotation</td>
<td valign="middle" align="center">90<break/>90<break/>90<break/>90<break/>90<break/>90<break/>90<break/>90</td>
<td valign="middle" align="center">23% &gt; NT<break/>7.29 - 11.83<break/>8.78 - 9.91<break/>6.73 - 9.72<break/>30% &gt;MOM</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B11">Fatumah et&#xa0;al., 2021</xref>)<break/>(Ghana)</td>
<td valign="middle" align="center">Ferric Acrisol</td>
<td valign="middle" align="center">Conventional Tillage and stover</td>
<td valign="middle" align="center">0</td>
<td valign="middle" align="center">3.29 &#x2013; 7.71</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>)<break/>(South Africa)</td>
<td valign="middle" align="center">Eutric Cambisol</td>
<td valign="middle" align="center">Conventional tillage<break/>No Till<break/>Residues removed<break/>Residue retained<break/>Biochar incorporation<break/>Maize -Wheat-Maize rotation<break/>Maize &#x2013; Wheat-Soy bean<break/>Maize &#x2013; Fallow-Maize<break/>Maize-Fallow-Soy bean</td>
<td valign="middle" align="center">90<break/>90<break/>90<break/>90<break/>90<break/>90<break/>90<break/>90<break/>90</td>
<td valign="middle" align="center">1.25 &#x2013; 18.70<break/>1.06 &#x2013; 15.41<break/>7.03 &#x2013; 11.85<break/>8.78 &#x2013; 9.92<break/>6.73 &#x2013; 9.76<break/>13.62 &#x2013; 14.38<break/>12.49 &#x2013; 13.24<break/>11.3<break/>10.97</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B56">Vilakazi et&#xa0;al., 2021</xref>)<break/>(South Africa)</td>
<td valign="middle" align="center">Ferralsol</td>
<td valign="middle" align="center">Conventional Tillage Control<break/>Conventional Tillage<break/>Conventional Tillage<break/>No Till Control<break/>No Till<break/>No Till</td>
<td valign="middle" align="center">0<break/>120<break/>240<break/>0<break/>120<break/>240</td>
<td valign="middle" align="center">2.84 &#x2013; 3.24</td>
<td valign="middle" align="center">0.07 &#x2013; 0.09<break/>0.05 &#x2013; 0.34</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B15">Hickman et&#xa0;al., 2014</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Humic Nitisols</td>
<td valign="middle" align="center">No N Control<break/>Moderate N input<break/>Intermediate N input<break/>Optimal N inptu<break/>High N input</td>
<td valign="middle" align="center">0<break/>50<break/>75<break/>100<break/>200</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.71 &#x2013; 0.98<break/>0.67 &#x2013; 0.80<break/>0.62 &#x2013; 0.63<break/>0.58 &#x2013; 0.62<break/>0.81 &#x2013; 1.39</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B28">Macharia et&#xa0;al., 2020</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Xanthic Ferralsol</td>
<td valign="middle" align="center">No N Control<break/>Inorganic fertiliser<break/>Goat manure<break/>Goat manure+inorganic fertiliser</td>
<td valign="middle" align="center">0<break/>120<break/>120<break/>60 + 60</td>
<td valign="middle" align="center">1.32 &#x2013; 1.47<break/>1.80 &#x2013; 2.02<break/>3.46 &#x2013; 3.69<break/>2.54 &#x2013; 2.87</td>
<td valign="middle" align="center">0.05 &#x2013; 0.21<break/>0.26 &#x2013; 0.52<break/>1.10 &#x2013; 1.34<break/>0.39 &#x2013; 0.87</td>
<td valign="middle" align="center">-0.17 - -0.05<break/>-1.12&#x2014;0.60<break/>-0.12 - -{{-}}-.06<break/>-1.22 - -0.84</td>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B49">Sommer et&#xa0;al., 2016</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Acric Ferralsol</td>
<td valign="middle" align="center">Farmyard manure+maize stover+Maize-legume rotation<break/>Farmyard manure+continuous maize<break/>Maize stover+continuous maize</td>
<td valign="middle" align="center">30<break/>0<break/>90</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">5.3 &#x2013; 8.7<break/>3.0 &#x2013; 4.0<break/>3.3 &#x2013; 3.4</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B34">Mosongo et&#xa0;al., 2022</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Chromic Vertisol</td>
<td valign="middle" align="center">No N Control<break/>Maize with mineral fertiliser<break/>Irrigated Maize<break/>Irrigated Maize and Manure<break/>Maize intercropped with legumes</td>
<td valign="middle" align="center">0<break/>100<break/>0<break/>40<break/>0</td>
<td valign="middle" align="center">4.1 &#x2013; 5.0<break/>4.1 &#x2013; 5.5</td>
<td valign="middle" align="center">&#x2264;2.0<break/>0.25 &#x2013; 2.45<break/>0.72 &#x2013; 2.68</td>
<td valign="middle" align="center">-1.8 &#x2013; 0.0<break/>-1.83 &#x2013; 0.33</td>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B27">Macharia et&#xa0;al., 2021</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Xanthic Ferralsols</td>
<td valign="middle" align="center">No N control<break/>Inorganic Fertiliser<break/>Goat manure<break/>Fertiliser + Goat manure</td>
<td valign="middle" align="center">0<break/>120<break/>120<break/>60 + 60</td>
<td valign="middle" align="center">1.31 &#x2013; 1.46<break/>1.79 &#x2013; 2.01<break/>3.46 &#x2013; 3.69<break/>2.52 &#x2013; 2.87</td>
<td valign="middle" align="center">0.05 &#x2013; 0.21<break/>0.26 &#x2013; 0.52<break/>1.09 &#x2013; 1.34<break/>0.39 &#x2013; 0.87</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B38">Nyamadzawo et&#xa0;al., 2017</xref>)<break/>(Zimbabwe)</td>
<td valign="middle" align="center">Haplic Lixisol</td>
<td valign="middle" align="center">No N control<break/>Inorganic Fertiliser<break/>Inorganic Fertiliser<break/>Fertiliser + Manure</td>
<td valign="middle" align="center">0<break/>60<break/>120<break/>60 + 60</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.32<break/>0.52<break/>0.41<break/>0.35</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B7">Chikowo et&#xa0;al., 2006</xref>)<break/>(Zimbabwe)</td>
<td valign="middle" align="center">Lixisol</td>
<td valign="middle" align="center">Sole Maize</td>
<td valign="middle" align="center">0</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.39</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B40">Ortiz-Gonzalo et&#xa0;al., 2018</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Nitisols</td>
<td valign="middle" align="center">Fertilised planting rows<break/>Unfertilized inter-rows</td>
<td valign="middle" align="center">100<break/>0</td>
<td valign="middle" align="center">5.57 &#x2013; 9.24<break/>4.83 &#x2013; 5.81</td>
<td valign="middle" align="center">0.56 &#x2013; 0.64<break/>0.10 &#x2013; 0.22</td>
<td valign="middle" align="center">-2.84 - -2.78<break/>-4.41 - - 3.38</td>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B55">Tully et&#xa0;al., 2023</xref>)<break/>(Kenya and Tanzania)</td>
<td valign="middle" align="center">Eutric Ferralsols &amp; Ferric Acrisols</td>
<td valign="middle" align="center">No N Control<break/>Moderate N input<break/>Intermediate N input<break/>Optimum N input<break/>High N input</td>
<td valign="middle" align="center">0<break/>50<break/>75<break/>100<break/>150</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.02 &#x2013; 1.40<break/>0.04 &#x2013; 3.60<break/>0.03 &#x2013; 3.30<break/>0.04 &#x2013; 1.90<break/>0.03 &#x2013; 3.50</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B17">Hickman et&#xa0;al., 2015b</xref>)<break/>(Kenya)</td>
<td valign="middle" align="center">Humic Nitisols</td>
<td valign="middle" align="center">No N Control, Moderate N input &amp;<break/>Intermediate N input<break/>Optimum N input<break/>High N input<break/>Very high N Input</td>
<td valign="middle" align="center">0, 50 &amp;75<break/>100<break/>150<break/>200</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">0.62 &#x2013; 0.71<break/>0.17 &#x2013; 0.71<break/>0.25 &#x2013; 0.29<break/>0.81</td>
<td valign="middle" align="center"/>
</tr>
<tr>
<td valign="middle" align="center">(<xref ref-type="bibr" rid="B11">Fatumah et&#xa0;al., 2021</xref>)<break/>(Uganda)</td>
<td valign="middle" align="center">Lixic Ferralsols</td>
<td valign="middle" align="center">Maize-Beans intercrop (mulched -NT)<break/>Maize-Beans intercrop (Non-mulched + Reduced Tillage)<break/>Maize-Beans intercrop + compost and reduced tillage)<break/>Sole Maize (Mulched &#x2013; NT)<break/>Sole Maize (Non-mulched + Tillage)<break/>Sole Maize + compost and reduced tillage</td>
<td valign="middle" align="center"/>
<td valign="middle" align="center">6.34<break/>8.59<break/>7.47<break/>8.23<break/>11.75<break/>9.67</td>
<td valign="middle" align="center">0.72<break/>0.80<break/>0.55<break/>0.86<break/>1.22<break/>0.55</td>
<td valign="middle" align="center">0.002<break/>-0.006<break/>-0.010<break/>0.001<break/>-0.008<break/>-0.013</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3_5">
<label>3.5</label>
<title>Management drivers of GHG emissions in maize systems</title>
<sec id="s3_5_1">
<label>3.5.1</label>
<title>Mineral N inputs and fertiliser management</title>
<p>Across the reviewed studies, nitrogen management consistently emerged as the dominant driver of GHG emissions from maize-based systems in SSA, particularly for N<sub>2</sub>O. Fertilised treatments generally exhibited higher N<sub>2</sub>O emissions than unfertilised controls, reflecting increased substrate availability for nitrification and denitrification (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>). Field experiments in western Kenya, for example, demonstrated clear increases in N<sub>2</sub>O fluxes following mineral fertiliser application, with pronounced emission pulses occurring shortly after fertilisation and during subsequent rainfall events (<xref ref-type="bibr" rid="B15">Hickman et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B14">Hickman et&#xa0;al., 2017</xref>). Similar patterns were reported in Tanzania and Ethiopia, where fertiliser-induced N<sub>2</sub>O emissions were strongly modulated by soil moisture dynamics (<xref ref-type="bibr" rid="B44">Raji and D&#xf6;rsch, 2020</xref>; <xref ref-type="bibr" rid="B55">Tully et&#xa0;al., 2023</xref>). Although average fertiliser application rates in SSA remain comparatively low, several studies reported nonlinear emission responses at higher N inputs. In maize systems receiving more than approximately 100 kg N ha<sup>&#x2212;1</sup>, N<sub>2</sub>O emissions increased disproportionately, particularly under wet soil conditions (<xref ref-type="bibr" rid="B44">Raji and D&#xf6;rsch, 2020</xref>). Long-term experiments in Kenya showed that N<sub>2</sub>O fluxes nearly doubled when fertiliser rates increased from moderate to high levels, without corresponding yield gains (<xref ref-type="bibr" rid="B15">Hickman et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B55">Tully et&#xa0;al., 2023</xref>). In contrast, split fertiliser applications improved synchrony between nitrogen availability and crop demand, reducing peak N<sub>2</sub>O emissions while maintaining or increasing maize yields (<xref ref-type="bibr" rid="B44">Raji and D&#xf6;rsch, 2020</xref>). These findings indicate that fertiliser management strategies that optimise timing and placement can substantially influence emission intensity, even under low-input systems.</p>
</sec>
<sec id="s3_5_2">
<label>3.5.2</label>
<title>Organic amendments and integrated nutrient management</title>
<p>The use of organic amendments, including animal manure and crop residues, modified GHG emission dynamics relative to mineral fertilisers by altering the timing and duration of nitrogen release. Across studies, organic N sources were associated with delayed and more prolonged N<sub>2</sub>O emission peaks, reflecting gradual mineralisation processes (<xref ref-type="bibr" rid="B30">Mapanda et al., 2012</xref>; <xref ref-type="bibr" rid="B27">Macharia et&#xa0;al., 2021</xref>). For instance, field trials in Kenya reported that manure-amended maize plots exhibited N<sub>2</sub>O emission peaks several days after application, in contrast to the rapid emission responses observed following mineral fertiliser use (<xref ref-type="bibr" rid="B22">Kimetu et&#xa0;al., 2006</xref>; <xref ref-type="bibr" rid="B38">Nyamadzawo et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B35">Musafiri et&#xa0;al., 2020a</xref>; <xref ref-type="bibr" rid="B56">Vilakazi et&#xa0;al., 2021</xref>). Integrated nutrient management approaches combining organic and inorganic inputs produced variable emission outcomes depending on soil texture, carbon availability, and moisture conditions (<xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>). In coarse-textured, well-drained soils with low organic carbon, Macharia et&#xa0;al (<xref ref-type="bibr" rid="B27">Macharia et&#xa0;al., 2021</xref>). reported increased N<sub>2</sub>O emissions following manure incorporation. The rise in emissions was attributed to enhanced microbial denitrification driven by the additional organic carbon, particularly during wetting events. Conversely, in fine-textured soils with higher carbon content, Musafiri et&#xa0;al (<xref ref-type="bibr" rid="B36">Musafiri et&#xa0;al., 2020b</xref>). found no significant emission increases after manure application. The quality of organic amendments further influenced emission outcomes. Manure from smallholder systems in SSA typically has a high C:N ratio and low nitrogen content compared to that in developed regions. Nyamadzawo et&#xa0;al (<xref ref-type="bibr" rid="B38">Nyamadzawo et&#xa0;al., 2017</xref>). demonstrated this in a comparative study between Zimbabwe and China, where low-quality manure (1.2&#x2013;1.4% N, dry basis) in Zimbabwe resulted in significantly lower N<sub>2</sub>O emissions than the high-quality manure used in China. Importantly, integrated nutrient management consistently improved maize yields relative to sole mineral fertilisation, and yield-scaled emissions often indicated comparable or improved environmental performance.</p>
</sec>
<sec id="s3_5_3">
<label>3.5.3</label>
<title>Tillage practices</title>
<p>Tillage intensity influenced GHG emissions through its effects on soil structure, aeration, and organic matter decomposition. Conventional tillage was generally associated with higher CO<sub>2</sub> emissions due to enhanced microbial decomposition of soil organic matter following soil disturbance. For example, studies from the Eastern Cape Province of South Africa reported 26.3% higher CO<sub>2</sub> fluxes under conventional tillage compared with no-tillage systems, particularly following rainfall events that stimulated microbial activity (<xref ref-type="bibr" rid="B26">Maccarthy et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B27">Macharia et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>). Reduced and no-tillage practices promoted soil carbon retention in surface layers and often reduced CO<sub>2</sub> emissions over time. However, their effects on N<sub>2</sub>O emissions were more variable. In some cases, no-tillage systems exhibited higher N<sub>2</sub>O fluxes during wet periods, as observed in maize trials in South Africa and Tanzania, where increased soil moisture and reduced aeration promoted denitrification (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>). When evaluated using global warming potential or yield-scaled emission metrics, reduced tillage systems generally outperformed conventional tillage, indicating net mitigation benefits despite occasional increases in individual gas fluxes (<xref ref-type="bibr" rid="B19">Kimaro et&#xa0;al., 2016a</xref>; <xref ref-type="bibr" rid="B3">Atakora et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B56">Vilakazi et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B52">Tegha et&#xa0;al., 2024</xref>).</p>
</sec>
<sec id="s3_5_4">
<label>3.5.4</label>
<title>Residue management</title>
<p>Residue management affected GHG emissions by modifying soil microclimate, moisture retention, and substrate availability for microbial processes. Residue retention generally increased soil moisture and reduced temperature fluctuations, creating favourable conditions for both microbial activity and carbon sequestration (<xref ref-type="bibr" rid="B35">Musafiri et&#xa0;al., 2020a</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B56">Vilakazi et&#xa0;al., 2021</xref>). Studies from South Africa and Tanzania reported higher short-term CO<sub>2</sub> and N<sub>2</sub>O emissions under residue-retained plots, particularly when residues were combined with mineral fertiliser (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>). Emission responses were strongly influenced by residue quality. In Tanzanian maize systems, the incorporation of maize stover with nitrogen fertiliser increased N<sub>2</sub>O emission factors, particularly under high water-filled pore space conditions. In contrast, studies using low-quality residues typical of SSA systems, characterised by high carbon-to-nitrogen ratios, reported reduced N<sub>2</sub>O emissions due to microbial nitrogen immobilisation and more complete denitrification to N<sub>2</sub> (<xref ref-type="bibr" rid="B8">Chikowo et&#xa0;al., 2007</xref>; <xref ref-type="bibr" rid="B40">Ortiz-Gonzalo et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>). Residues converted to biochar and applied to maize fields generally improved yields and reduced overall GHG emissions, although CO<sub>2</sub> fluxes were higher than in non-biochar controls in Nyambo et&#xa0;al (<xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>); however, the overall mitigation benefit remained evident when emissions were evaluated on a yield-scaled basis. Despite short-term increases in CO<sub>2</sub> and, in some cases, N<sub>2</sub>O, residue retention consistently increased soil organic carbon stocks, suggesting long-term mitigation potential when assessed over extended time horizons.</p>
</sec>
<sec id="s3_5_5">
<label>3.5.5</label>
<title>Crop diversification and rotations</title>
<p>Crop diversification through intercropping and rotation influenced GHG emissions by altering nitrogen inputs and soil biological activity. Legume intercropping systems often increased N<sub>2</sub>O emissions due to the addition of biologically fixed nitrogen, although emission magnitude varied by species and management (<xref ref-type="bibr" rid="B22">Kimetu et&#xa0;al., 2006</xref>). For example, field studies in Ethiopia reported higher N<sub>2</sub>O emissions under maize&#x2013;lablab intercropping compared with maize monocropping, while delayed intercropping significantly reduced emission intensity (<xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>). Additionally, emission responses also varied with legume species. For example, Lablab purpureus generated higher N<sub>2</sub>O emissions due to its high biomass and nitrogen fixation potential, whereas Crotalaria juncea was associated with lower emissions (<xref ref-type="bibr" rid="B43">Raji and D&#xf6;rsch, 2019</xref>). In contrast, crop rotations incorporating legumes generally improved yields and reduced emissions compared with continuous maize systems. Long-term experiments in South Africa demonstrated lower CO<sub>2</sub> emissions and improved soil carbon status under maize&#x2013;legume rotations relative to continuous cereal systems (<xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>). These findings suggest that rotational diversification may offer more stable mitigation benefits than intercropping in certain agroecological contexts, particularly when combined with optimised nitrogen management.</p>
</sec>
</sec>
<sec id="s3_6">
<label>3.6</label>
<title>Conservation agriculture and mitigation trade-offs in maize systems</title>
<p>Conservation agriculture, based on the principles of reduced soil disturbance, permanent soil cover, and crop diversification, is widely promoted in SSA as a climate-smart approach capable of enhancing productivity while reducing GHG emissions (<xref ref-type="bibr" rid="B19">Kimaro et&#xa0;al., 2016a</xref>). Evidence from the reviewed studies indicates that CA practices can influence emission dynamics through multiple interacting pathways, but their mitigation outcomes are strongly context dependent and often involve trade-offs among different gases and management objectives (<xref ref-type="bibr" rid="B19">Kimaro et&#xa0;al., 2016a</xref>; <xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B56">Vilakazi et&#xa0;al., 2021</xref>). Across studies, reduced or no-tillage systems consistently improved soil organic carbon retention and reduced CO<sub>2</sub> emissions relative to conventional tillage, particularly over longer time frames. Field experiments in South Africa and Tanzania, for example, reported lower CO<sub>2</sub> fluxes and higher soil carbon stocks under reduced tillage, reflecting reduced soil disturbance and slower organic matter decomposition (<xref ref-type="bibr" rid="B20">Kimaro et&#xa0;al., 2016b</xref>; <xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B37">Muzangwa et&#xa0;al., 2021</xref>). However, these benefits were not uniform across all conditions. In wetter environments or during prolonged rainfall periods, reduced tillage occasionally increased N<sub>2</sub>O emissions due to higher soil moisture and the formation of anaerobic microsites that favoured denitrification (<xref ref-type="bibr" rid="B39">Nyambo et&#xa0;al., 2020</xref>). These findings highlight a key trade-off in CA systems, where practices that promote carbon sequestration may simultaneously increase short-term N<sub>2</sub>O losses under certain environmental conditions. Residue retention, another core CA principle, further illustrates these trade-offs. Retaining crop residues generally enhanced soil moisture conservation and contributed to long-term soil carbon accumulation, but several studies reported short-term increases in CO<sub>2</sub> and N<sub>2</sub>O emissions following residue addition, particularly when residues were combined with nitrogen fertiliser. For example, maize stover retention in Tanzanian systems (<xref ref-type="bibr" rid="B6">Centre and Centre, 2008</xref>) increased N<sub>2</sub>O emissions during wet periods, while low-quality residues with high carbon-to-nitrogen ratios in other SSA systems promoted nitrogen immobilisation and reduced N<sub>2</sub>O losses. These contrasting outcomes highlight the importance of residue quality, soil texture, and fertiliser management in determining emission responses. Crop diversification through rotations or intercropping influenced CA mitigation outcomes by altering nitrogen inputs and residue dynamics. While legume intercropping increased N<sub>2</sub>O emissions in some studies due to biological nitrogen fixation, rotational systems incorporating legumes generally improved yields and reduced overall emissions compared with continuous maize monocropping. Long-term rotation trials in southern Africa demonstrated lower global warming potential and improved yield-scaled emissions under diversified systems, suggesting that rotation-based diversification may offer more consistent mitigation benefits than intercropping alone. Importantly, when mitigation outcomes were evaluated using yield-scaled metrics rather than absolute emissions, CA systems frequently performed better than conventional systems. Studies in Tanzania and South Africa showed that although absolute N<sub>2</sub>O emissions were sometimes higher under CA practices, improved yields and soil carbon sequestration resulted in lower emission intensity per unit of grain produced (<xref ref-type="bibr" rid="B8">Chikowo et&#xa0;al., 2007</xref>; <xref ref-type="bibr" rid="B3">Atakora et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B58">Zheng et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B11">Fatumah et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B52">Tegha et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B2">Alasinrin et&#xa0;al., 2025</xref>). This finding emphasises that assessments of CA mitigation potential should account for productivity outcomes alongside emission measurements. Overall, the reviewed evidence indicates that CA holds significant potential to contribute to GHG mitigation in maize-based systems of SSA, but its effectiveness depends on the specific combination of practices implemented and their alignment with local soil and climatic conditions. Rather than delivering uniform emission reductions, CA practices influence emissions through complex interactions that require site-specific management and long-term evaluation. These insights reinforce the need to assess CA systems holistically, integrating emissions, soil carbon dynamics, and productivity to identify context-appropriate climate-smart strategies.</p>
</sec>
<sec id="s3_7">
<label>3.7</label>
<title>Evidence gaps and synthesis priorities for maize GHG research in SSA</title>
<p>Despite the growing body of research on GHG emissions from maize-based systems in SSA, important evidence gaps and synthesis challenges remain. These gaps do not reflect a lack of agronomic or environmental research in the region, but rather the fragmented nature of existing studies, which differ widely in spatial coverage, experimental duration, measurement scope, and methodological approaches. A key limitation of the current evidence base is the strong geographic concentration of field-based GHG studies in a small number of countries, particularly in East and Southern Africa. Large maize-producing regions in West and Central Africa remain underrepresented in experimental emission measurements, limiting the ability to generalise findings across the region&#x2019;s diverse agroecological zones. Expanding field-based measurements to these underrepresented regions would substantially improve regional emission estimates and mitigation assessments. Temporal limitations also constrain synthesis. Most studies are short-term, often spanning one to three growing seasons, and therefore capture only a limited range of climatic variability. Given the strong influence of rainfall, soil moisture, and temperature on emission dynamics, longer-term experiments are required to assess interannual variability and the persistence of mitigation outcomes under changing climate conditions. While individual components of conservation agriculture have demonstrated mitigation potential, their combined and long-term effects remain insufficiently quantified across diverse SSA environments. Addressing these gaps will require coordinated, multi-site, long-term experiments that integrate biophysical measurements with productivity and soil health indicators. Such efforts are essential for developing context-specific, climate-smart maize production strategies that balance food security and greenhouse gas mitigation objectives in Sub-Saharan Africa.</p>
</sec>
</sec>
<sec id="s4">
<label>4</label>
<title>Potential limitations of the review</title>
<p>While this review provides valuable insights into GHG emissions from maize-based systems in SSA, several limitations should be acknowledged. The synthesis was restricted to published field-based experimental studies reporting direct GHG measurements, which may have excluded a broader body of agronomic, modelling, and soil carbon research that offers complementary insights into mitigation-relevant processes; such studies were therefore considered only for contextual interpretation. In addition, the spatial coverage of the reviewed studies was uneven, with research concentrated in a limited number of countries, potentially limiting representation of the full diversity of agroecological conditions, management practices, and socio-economic contexts across the region. Furthermore, the reviewed literature primarily reflects smallholder farming systems, which dominate maize production in SSA, while the contributions of more intensive systems&#x2014;although present to a lesser extent&#x2014;were not explicitly captured. Despite these limitations, the review provides a robust synthesis of available evidence and identifies key priorities for future research. Addressing these gaps through more geographically inclusive, methodologically integrated, and long-term studies will be essential for improving understanding of GHG emission dynamics and supporting the development of context-specific mitigation strategies for SSA.</p>
</sec>
<sec id="s5" sec-type="conclusions">
<label>5</label>
<title>Conclusion and recommendation</title>
<p>This review synthesised field-based experimental evidence on GHG emissions from maize-based agroecosystems in SSA, with emphasis on emission characteristics, key management drivers, and the mitigation potential of conservation-oriented practices. The reviewed studies collectively indicate that GHG emissions from maize systems in SSA are generally lower than those reported in high-input systems elsewhere, largely reflecting low nitrogen inputs and prevailing environmental conditions. Across systems, N<sub>2</sub>O consistently emerged as the dominant contributor to climate forcing, while CO<sub>2</sub> and CH<sub>4</sub> fluxes were strongly regulated by soil disturbance, residue management, and hydrological conditions. Management practices exerted a strong influence on emission dynamics, but their effects were highly context dependent. Nitrogen input rate and timing were the primary determinants of N<sub>2</sub>O emissions, with nonlinear emission responses observed at higher fertiliser levels. Reduced tillage and residue retention promoted soil carbon accumulation and often reduced CO<sub>2</sub> emissions, although short-term increases in N<sub>2</sub>O were reported under wet conditions. Crop diversification, particularly through rotations incorporating legumes, generally improved productivity and reduced emissions relative to continuous maize monocropping, while intercropping outcomes varied with species, timing, and nitrogen management. When evaluated using yield-scaled metrics, conservation agricultural practices frequently demonstrated improved environmental performance despite occasional increases in absolute emissions. Although conservation agriculture shows clear potential to contribute to climate-change mitigation in maize systems of SSA, its effectiveness depends on the specific combination of practices implemented and their alignment with local soil and climatic conditions. Rather than delivering uniform emission reductions, conservation agriculture influences GHG emissions through interacting biophysical processes that require site-specific management and long-term evaluation. Several synthesis priorities emerge from this review. Future research should expand field-based GHG measurements to underrepresented regions, particularly West and Central Africa, and prioritise long-term, multi-site experiments capable of capturing climatic variability. Greater integration of multiple greenhouse gases, soil carbon dynamics, and productivity outcomes within the same experimental frameworks is needed to enable robust assessment of trade-offs and mitigation potential. Explicit consideration of environmental drivers&#x2014;such as soil texture, moisture, and pH&#x2014;will further improve the transferability of management recommendations. Advancing climate-smart maize production in SSA will require coordinated research efforts that integrate biophysical measurements with agronomic performance and soil health indicators. Such evidence is essential to support the development of context-specific mitigation strategies that balance food security, resilience, and greenhouse gas reduction objectives across the region.</p>
</sec>
</body>
<back>
<sec id="s6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material. Further inquiries can be directed to the corresponding author.</p></sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>CM: Data curation, Conceptualization, Writing &#x2013; review &amp; editing, Validation, Writing &#x2013; original draft, Methodology, Formal analysis. OO: Validation, Writing &#x2013; review &amp; editing, Formal analysis, Supervision, Visualization, Methodology, Writing &#x2013; original draft, Conceptualization. JD: Validation, Supervision, Writing &#x2013; review &amp; editing, Methodology, Investigation. RL: Supervision, Writing &#x2013; review &amp; editing, Investigation, Project administration, Visualization, Data curation. PN: Supervision, Writing &#x2013; review &amp; editing. JC: Writing &#x2013; review &amp; editing, Supervision. AL-L: Resources, Supervision, Validation, Writing &#x2013; review &amp; editing. LC: Resources, Conceptualization, Writing &#x2013; review &amp; editing, Project administration, Supervision.</p></sec>
<sec id="s9" sec-type="COI-statement">
<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 id="s10" sec-type="ai-statement">
<title>Generative AI statement</title>
<p>The author(s) declared that generative AI was not used in the creation of this manuscript.</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 id="s11" sec-type="disclaimer">
<title>Publisher&#x2019;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>
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<fn id="n1" fn-type="custom" custom-type="edited-by">
<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1677399">Ivan Vasenev</ext-link>, Moscow Timiryazev Agricultural Academy, Russia</p></fn>
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<p>Reviewed by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3294404">Iskid Jacquet</ext-link>, China University of Geosciences (Beijing) Energy Institute, China</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3300726">Theophilus Olufemi Isimikalu</ext-link>, University of Maryland Eastern Shore, United States</p></fn>
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