Batwa communities inhabiting Uganda's complex topography lack timely access to climate information services (CISs) due to scarce meteorological stations. Tailoring historical satellite data to local spatio-temporal dimensions is central to catalyzing sustainable development goals (SDGs). This study employed satellite data from 1983 to 2023 to inform sustainable and climate-smart decision-making for the Batwa communities in southwestern Uganda. Daily precipitation (DPR) and air temperature data were obtained from the Climate Hazard Group Infrared Precipitation with Station (CHIRPS) and the NASA Power website (NASAPW), respectively. ClimPACT3 model was employed to generate climate indices (CIs) while R-Instat was utilized to perform statistical analysis. Results revealed that the area experiences wetter than normal conditions, with precipitation (PR) ranges of 1,006–1,489 mm. A significant (p-value < 0.05) increase in the annual sum of daily precipitation (ASDPR) > the 95th percentile was observed. The daily minimum temperature (DTMin.) and maximum temperature (DTMax.) ranged from 13.1 to 14.5 °C and 24.0 to 26.4 °C, respectively. The current study connected the implications of the results to the broader SDGs. The synergies between SDG 13 and other SDGs were also established. Therefore, the study's outcomes are imperative in advancing climate resilience for the agricultural, health, and water resources sectors.

  • Satellite datasets were used to assess fluctuations in CIs, while RH-tests were used for DQCD.

  • ClimPACT3 and R-Instat used for CIs and statistical analyses, respectively.

  • Implications of the findings connected to the broader SDGs and climate resilience.

  • Knowledge of variations in extreme CIs could advance SDG 13 (climate action).

  • Implementing SDG 13 could contribute to the achievement of other SDGs.

A valuable tool for improving sustainable development is historical weather and climate data (HWCD), which, when properly utilized, can enhance the lives of vulnerable communities susceptible to climate change impacts (CCIs) (Dinku et al. 2018). Batwa communities, in the highlands of Kigezi-southwestern Uganda, are particularly vulnerable to climatic threats such as flash floods (FFs), soil erosion, and disease incidence (van Bavel et al. 2020). The frequency of these climate hazards has intensified of late, posing more danger to this Indigenous group (Satyal et al. 2021). The fact that over 70% of the Batwa households live in perpetual deficiency of basic needs such as food, housing, clothing, and education raises concern (Scarpa et al. 2021), especially in the face of a changing climate. The hilly, solitary, and remote terrains in which they live further exacerbate the challenge (Luliro et al. 2022). Harnessing HWCD is essential for these indigenous communities since it facilitates climate-sensitive early-warning system design, planning, research, and the identification of climate risks such as catastrophic weather events. Additionally, the HWCD provides a baseline for future climate projections as well as establishing the climate change (CC) trajectory (Ngoma et al. 2021).

Considering statistics indicating that Africa is the continent most exposed to CCIs (IPCC 2023), harnessing the HWCD becomes even more essential to investigate changes in climate indices (CIs) for early-warning purposes. This should receive the utmost interest since the majority of African economies depend on climate-sensitive industries like agriculture for development. About 80% of agriculture worldwide is rain-fed, according to Dinku (2019), and in Africa, this percentage exceeds 95%. In Africa, agriculture contributes significantly to GDP and provides a living for a larger proportion of the continent's rural population. The application of HWCD in location-specific local contexts would be crucial for African nations to meet their nationally established development plans and the 2030 Agenda SDGs (Dorward et al. 2020). This is due to the fact that successful CC adaptation techniques are frequently context-specific, taking into account local sociocultural, sectoral, and geographic variables that differ from place to place.

Exploitation of the HWCD in Africa is inadequate because the majority of National Meteorological and Hydrological Services (NMHS) gather the data with poor quality checks, thus reducing its relevance to the local community (Dinku 2019). Faniriantsoa & Dinku (2022) reported that the primary challenge to climate data availability and quality in Africa is attributed to a sparse and uneven distribution network of weather stations. The coverage is typically lower in rural areas, where livelihoods are most vulnerable to the adverse impacts of CC. Other problems included low-quality station observations with many missing data points and the inaccessibility of the NMHS's available data. Dinku (2019) claims that insufficient dissemination tools and capacity, scarce resources, and other factors make data accessibility in Uganda a major challenge. In order to overcome these challenges, the present investigation employed rainfall and temperature datasets from CHIRPS and NASAPW, respectively. The selection was based on the datasets' free accessibility, high resolution, and global coverage, which provide a more dependable and contextualized outlook at the local level (Dhanesh et al. 2020; Halimi et al. 2023; Tan et al. 2023; Du et al. 2024).

Furthermore, in a nation where accessing data remains a fundamental challenge (Ngoma et al. 2021), strategizing on the utilization of the HWCD would facilitate sustainably informed decisions for building climate-resilient communities. Numerous studies evaluating and analysing HWCD trends have surfaced recently, but the majority of them concentrate on larger spatial scales, such as regional (Githumbi et al. 2020), national (Egeru et al. 2019; Nuwagira & Yasin 2022), and some even considering continental (Nash et al. 2016; Ayugi et al. 2022). Previous studies have solely concentrated on sector-specific aspects while ignoring the multi-dimensional facets of the SDGs (Luliro et al. 2022). Studies aimed at assessing HWCD in a local context are inadequate, and none that focus on using historical climatology to benefit the Batwa indigenous population, inhabiting intricate hilltops of southwestern Uganda, have been found in peer-reviewed literature. Incoherent understanding of the past climatic patterns experienced by the Batwa people increases the possibility of maladaptation or resource mismanagement in the context of climate adaptation initiatives. Conversely, recognizing the local changes in meteorological parameters, especially in a complex geomorphology, is crucial for devising suitable proactive mitigation approaches and augmenting farming output (Etana et al. 2020). Consequently, leading to the realzation of multifarious SDG targets (SDGTs). Furthermore, the terrain of southwestern Uganda is renowned for being incredibly complex, with elevations spanning from 912 to 3019 m above sea level (see Figure 1). The Batwa agrarian community exploring feasible local approaches to combat the CCIs and fluctuations may find minimal value in national or regional analyses, which are unable to capture local alteration in meteorological variables due to the great spatial diversity in the landscape. Hence, tailoring the analysis to the local setting renders the data more applicable for the farmers to implement preventative actions for adverse CCIs (Etana et al. 2020). To the best of our knowledge, this is the first study to use the ClimPACT3 model to investigate fluctuations in extreme CIs in a mountainous topography using RS data from the NASAPW and the CHIRPS toward climate resilience advancement. So, what makes this research unique is that it uses open-source ClimPACT3 and R-Instat models to assess fluctuations in extreme CIs in a complicated landscape using RS data from the NASAPW and the CHIRPS and connect the implications to the broader 2030 SDGs. The current study aims to achieve the following precise goals: (1) to employ satellite data from the CHIRPS and the NASAPW to assess extreme CIs using open-source ClimPACT3; (2) to perform statistical analysis of the HWCD using R-Instat; (3) to interlink the implications of the findings with the broader SDGs; and (4) to identify the synergies between SDG 13 (climate action) and other SDGs. This study bridges the gap between climate science and local, practical solutions to advance sustainable development by particularly tailoring HWCD to the needs of the Batwa indigenous community using the ClimPACT3 tool and R-Instat software. The study's outcomes provide a baseline for stakeholders to identify potential climate threats based on emerging trends, prepare appropriate adaptation strategies to manage future climate variability contingent on historical patterns and make well-informed decisions for optimal resource utilization.
Figure 1

Study area location map of major districts harbouring Batwa communities in southwestern Uganda.

Figure 1

Study area location map of major districts harbouring Batwa communities in southwestern Uganda.

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Study area description

The study focused on Kabale, Kanungu, and Kisoro (KAKAKI) districts of southwestern Uganda (see Figure 1). The geographical latitudes and longitudes of the study area are −1.5° S to −0.3° S and 29.4° E to 30.3° E, respectively. The area is inhabited by a significantly greater number of Batwa communities. The study area is bounded by Ntungamo to the east, the Democratic Republic of Congo to the west, Rukungiri to the north, and Rwanda to the south. According to Satyal et al. (2021), Batwa settlements are scattered throughout the hilly, solitary, and remote parts of these districts, comprising 10–20 households. These areas are frequently susceptible to climatic threats such as FFs, soil erosion, and disease incidence (van Bavel et al. 2020). A study by Scarpa et al. (2021) revealed that about 70% deficiency in basic living standards prevails among the Batwa people. The study location is situated in the tropical Savannah climate zone, with a bimodal (MAM and SOND) rainy season each year. The major crops produced under the rain-fed farming system in the area include Irish potatoes, bananas, coffee, sweet potatoes, beans, and cereals (Scarpa et al. 2021).

Acquisition of the HWCD

Retrieving precipitation data

The traditional methods for measuring rainfall at the local level are rain gauges and weather radars (Shahid et al. 2021). However, because of their limited distribution throughout the research area, it is difficult to record the spatio-temporal variability in precipitation, particularly in the Kigezi region's mountainous areas. The employed daily precipitation data was obtained from CHIRPS, which is accessible at https://app.climateengine.org/climateEngine. The preference for CHIRPS data is attributable to its high resolution (0.05° × 0.05°) and its integration of satellite imagery with ground station data, offering a more comprehensive raster and reliability (Basheer & Elagib 2019; Dhanesh et al. 2020; Du et al. 2024). A study by Shahid et al. (2021) affirms that CHIRPS precipitation data reliably complements ground station data in addition to providing continuous precipitation monitoring over large temporal and spatial scales. Moreover, CHIRPS provides free daily datasets available for extended periods dating back to 1981. To download the precipitation data (PRD), the area of interest was initially zoomed in and a polygon drawn to represent it on the map. Additionally, the CHIRPS 4.8 km dataset was selected under the ‘climate and hydrology’ section, and the ‘variable’ section was modified to ‘precipitation.’ The units were set to ‘milimetres,’ while the ‘statistics’ section was set to ‘total’ to indicate cumulative precipitation. The required data's time period was adjusted to range from January 1, 1983 to December 31, 2023. A graph was generated by clicking on ‘Get Time Series,’ and after clicking on the ‘download button’ in the top right corner of the graph, the PRD was downloaded as a CSV file (Obura et al. 2024c). These steps were repeated for each of the three KAKAKI districts containing the Batwa. Eventually, an average of the three districts was obtained to serve as the representative rainfall dataset.

Obtaining temperature data

The NASAPW was exploited to retrieve the DTMin. and DTMax. datasets at 2 m from https://power.larc.nasa.gov/data-access-viewer/. The NASAPW is a comprehensive, freely accessible, and dependable satellite data source for temperature with high resolution and global coverage, which enables studies to be conducted even on a local scale. NASA implements stringent quality control procedures to guarantee the accuracy of its data. Furthermore, numerous studies have reported on the validity and reliability of NASAPW TED (Aboelkhair et al. 2019; Marzouk 2021; Carrara et al. 2023; Halimi et al. 2023; Tan et al. 2023). The user community ‘Agroclimatology’ was chosen after opening the ‘data access viewer’ on the NASAPW in order to download temperature data (TED). Each of the three KAKAKI districts' lat/long coordinates was input, and the temporal average was set to ‘daily.’ The output file format was set to CSV, and the timeframe was set from January 1, 1983, to December 31, 2023. The minimum and maximum temperatures (MMTs) were nominated for download when the ‘Temperatures/Thermal IR Flux’ section under the ‘Select Parameters’ section was opened. After pressing the ‘Submit’ button, daily native resolution NASA Power (NASAP) CERES/MERRA-2 data was downloaded in a CSV format (Obura et al. 2024c). The MMTs were represented by averaging the three district datasets.

Data quality control diagnostics

The consistency and quality of the daily input data were checked before the indices were computed. A crucial requirement for a robust analysis of climate time series is homogeneity. This study adopted free and user-friendly RH-tests software to perform the data quality control diagnostics (DQCD). Based on the penalised maximal t-test (PMT) or f-test (PMF), the programme can identify and correct multiple change points in a time series, as demonstrated by J. Du et al. (2020) and validated by Liu et al. (2017). Reference stations are necessary for PMT when conducting a homogeneity study, but PMF can be employed as an absolute approach, which means it can be used in isolation or in the absence of neighbouring stations for comparison. Therefore, the PMF method was used in this investigation.

Determining the CIs

The CIs required to comprehend the climatology of the study location were generated utilising ClimPACT v3.1.6 in this investigation. ClimPACT3 is an open-source tool programmed by the Expert Team on Sector-specific Climate Indices (ET-SCI) for the World Meteorological Organisation (WMO). ClimPACT v3.1.6 was chosen because it allows for customization based on local conditions, enhancing the relevance of findings for a specific region (Murara & Mendonça 2019; Dubey et al. 2022). It is also incorporated with diverse internationally recognized CIs for determining precipitation extremes, heat waves, and cold waves, making it a reliable tool for long-term climate data analysis (Nakaegawa & Murazaki 2022). Furthermore, ClimPACT integrates with various climate data formats, promoting wide applicability, supporting research, and climate adaptation planning (WMO 2016). It employs daily parameters against monthly datasets because several significant pieces of information are concealed in monthly climate data, which may be crucial to multiple fields, including agriculture, health, and water resources. Employing daily data to produce CIs provides a comprehensive understanding of multiple variables, including the periodicity and intensity of extreme rainfall and measurements of extremely wet, dry, hot, or cold periods that influence society's economy.

Furthermore, the Mann–Kendall test at 0.05 and Sen's slope estimator were adopted for trend analysis (Agarwal et al. 2021; van der Walt & Fitchett 2021; Şen & Şişman 2023). Ten (10) indices (see Table 1) implemented in this investigation were nominated based on their significance to health (H), agriculture and food security (AFS), as well as water resources and hydrology (WRH). By capturing significant trends and anomalies, CIs helps in summarizing complex climate data to inform decision-making in sectors such as agriculture, health, and water management. In addition, the Standardized Precipitation Evapotranspiration Index (SPEI) was selected in contrast to the Standardized Precipitation Index (SPI) due to its ability to amalgamate the multi-temporal nature of the SPI with its computational simplicity and sensitivity to changes in evaporative demand ignited by temperature trends and fluctuations (Vicente-Serrano et al. 2010). The WMO approved the SPEI as the reference drought index for more effective determination of drought sensitivity and climate risk management of drought hazards on sensitive systems (Mishra & Aadhar 2021).

Table 1

Description of ET-SCI indices adopted for the current study

ET-SCI indexDescriptionUnitsSector(s)
SPEI A drought metric based on Evaporation and PR. Unit-less H, AFS, WRH 
Consecutive Dry Days (CDDs) Maximum number of CDDs when PR < 1.0 mm. Days H, AFS, WRH 
Consecutive Wet Days (CWDs) Maximum number of CWDs per year when PR ≥ 1.0 mm. Days H, AFS, WRH 
Annual Total wet-day rainfall (PRCPTOT) Sum of daily PR ≥ 1.0 mm mm AFS, WRH 
PR20mm Days on which PR ≥ 20 mm Days AFS, WRH 
Max 1-day PR (Rx1day) Maximum amount of rain that falls in 1-day mm H, AFS, WRH 
PR95p ASDPR > the 95th Percentile. mm AFS, WRH 
DTMin. Daily minimum temperature °C H, AFS 
Daily Temperature Range (DTR) Daily range of maximum and minimum temperature °C H, AFS, WRH 
DTMax. Daily maximum temperature °C H, AFS 
ET-SCI indexDescriptionUnitsSector(s)
SPEI A drought metric based on Evaporation and PR. Unit-less H, AFS, WRH 
Consecutive Dry Days (CDDs) Maximum number of CDDs when PR < 1.0 mm. Days H, AFS, WRH 
Consecutive Wet Days (CWDs) Maximum number of CWDs per year when PR ≥ 1.0 mm. Days H, AFS, WRH 
Annual Total wet-day rainfall (PRCPTOT) Sum of daily PR ≥ 1.0 mm mm AFS, WRH 
PR20mm Days on which PR ≥ 20 mm Days AFS, WRH 
Max 1-day PR (Rx1day) Maximum amount of rain that falls in 1-day mm H, AFS, WRH 
PR95p ASDPR > the 95th Percentile. mm AFS, WRH 
DTMin. Daily minimum temperature °C H, AFS 
Daily Temperature Range (DTR) Daily range of maximum and minimum temperature °C H, AFS, WRH 
DTMax. Daily maximum temperature °C H, AFS 

Statistical analysis of the HWCD

The HWCD in CSV format for the study location was imported and analysed in R-Instat 0.7.16.50. The data was checked, reshaped, and arranged using the ‘prepare’ tab. Then, the ‘climatic’ tab was applied to prepare climatic summaries and determine the onset and cessation of the rains and the duration of each season. Furthermore, the statistical analysis was performed for the bimodal rainy seasons using R-Instat. The criterion to establish the rainy season's onset was set to three consecutive days with total precipitation (TPR) ≥ 20 mm and the absence of nine consecutive dry days (CDDs) in the first 21 days. Onset dates were established for the MAM and SOND seasons. The last day of the season to receive the PR > 10 mm was designated as the the season’ cessation. Finally, the output from R-Instat was exported to an Excel spreadsheet for additional modification, where plots for seasonal TPR and the extent of each season were generated. R-Instat was selected for this study because of its easy-to-use interface, which makes complicated statistical processes simpler. It offers quality control tools and also accomodates huge climatic datasets. Advanced statistical techniques like regression, time series analysis, and climatic trend evaluations are integrated into the software, simplifying analysis. R-Instat is an open-source and free software (Fundi et al. 2024), making it easily accessible for use in this study.

Exploration of the SPEI temporal patterns

The time series (1983–2023) trends of every SPEI extreme CI category were examined in this subsection. Despite the absence of similar reports that were specific to the study location, the SPEI categories in Figure 2 demonstrated a significantly positive trend (1983–2023). In each scenario, the Sen's slope value is positive and the p-value is zero. Moreover, Sen's slope for SPEI 24 is 0.005, indicating a significantly positive trend, whereas Sen's slope for SPEI 3 is 0.002, indicating a modest positive trend. The positive trajectory in both situations demonstrates that daily, monthly, or annual PR around the study location exceeds potential evapotranspiration. This implies that the area generally experiences wetter than average weather. The last 5 years of study (i.e., 2018–2023) saw the SPEI value range from 1.50 to 1.99, representing a severely wet scenario (see Table 2). Furthermore, the positive SPEI pattern could be allied to parameters like higher humidity or lower temperatures, which decrease the evapotranspiration rate. Although this result suggests a reduced drought risk, it exposes the study area to greater flooding susceptibility because of the heterogeneous terrain.
Table 2

SPEI classification according to Omondi & Lin (2023) 

SPEI rangeDrought description
SPEI ≤ −2.00 Extremely dry 
−1.99 ≤ SPEI ≤ −1.50 Severely dry 
−1.49 ≤ SPEI ≤ −1.00 Moderately dry 
−0.99 ≤ SPEI ≤0.99 Near normal 
1.00 ≤ SPEI ≤1.49 Moderately wet 
1.50 ≤ SPEI ≤1.99 Severely wet 
SPEI ≥ 2.00 Extremely wet 
SPEI rangeDrought description
SPEI ≤ −2.00 Extremely dry 
−1.99 ≤ SPEI ≤ −1.50 Severely dry 
−1.49 ≤ SPEI ≤ −1.00 Moderately dry 
−0.99 ≤ SPEI ≤0.99 Near normal 
1.00 ≤ SPEI ≤1.49 Moderately wet 
1.50 ≤ SPEI ≤1.99 Severely wet 
SPEI ≥ 2.00 Extremely wet 
Figure 2

Time evolution of (a) SPEI 3, (b) SPEI 6, (c) SPEI 12, and (d) SPEI 24 categories. The straight red line represents the linear regression in the time series (1983–2023).

Figure 2

Time evolution of (a) SPEI 3, (b) SPEI 6, (c) SPEI 12, and (d) SPEI 24 categories. The straight red line represents the linear regression in the time series (1983–2023).

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A significantly positive SPEI could be valuable for agricultural productivity by increasing soil moisture and water availability, favouring crop growth. This has a positive implication on SDG 2 (Zero Hunger) and especially contributes to achieving SDGTs 2.1, 2.2, and 2.3. In the WRH sector, a positive SPEI trend could improve water supplies but also calls for the improved infrastructural need to manage the excess water. This has direct implications for the efforts to achieve SDGTs 6.1, 6.2, and 6.3. Healthwise, wetter than usual conditions pose significant health risks, including the emergence of water- and vector-borne diseases, communicable diseases, and psychological disorders due to the evacuation of people from flood-vulnerable zones. A study by van Bavel et al. (2020) claims that increased moisture, which supports larger mosquito populations and other insects that spread diseases like dengue fever and the West Nile virus, is a contributing factor in the proliferation of vector-borne diseases in wetter environments. This calls for concerted and prioritized efforts from relevant stakeholders since a laxity directly hampers the achievement of target 3.3 of SDG 3 (Healthy lives and well-being for all).

Temporal variations in PR

The ASDPR for the region is significantly increasing with substantial variability, as observed in Figure 3(a). The p-value is 0.038, whereas the Sen's slope value is 3.277, indicating a highly positive trend. The annual normal average rainfall received around the area is 1,204 mm, with the minimum annual rainfall of 1,006 mm received in 1993 and the maximum rainfall of 1,489 mm received in 2018. Figure 3(b) indicates a significantly growing trend in the annual count of days with PR ≥ 20 mm, with 2020 registering the highest number of days (12 days). The maximum amount of PR that occurs in a single day (PR*1 day) has been fluctuating from 1983 to 2023, as observed in Figure 3(c). Moreover, the year 2004 recorded the lowest PR*1 day of 19 mm, while 2023 registered the highest value of 62 mm. On average, each year records a day with a maximum PR amount of 34 mm. Although insignificant (p-value = 0.537), PR*1 day has been increasing with a positive Sen's slope value of 0.065. Contrarywise, Figure 3(d) shows a significant (p-value < 0.05) increase in the ASDPR > the 95th percentile with a positive Sen's slope value of 3.189. Furthermore, the percentage contribution of very wet days to the total wet-day rainfall is increasing substantially. An increase in more intense PR events in KAKAKI districts has been allied with more occurrences of FFs, increased soil erosion and leaching (SEL), as well as landslides in hilly areas in the recent past (Kanyiginya et al. 2023). Augmented SEL is responsible for a substantial reduction in soil fertility, hence lowering agricultural yields (Aslam et al. 2021), while FFs and landslides cause human death, damage physical infrastructure like highway bridges, disrupt operation of economic activities, and destroy agricultural areas, thus reducing the country's gross domestic product (SDGTs 11.1–11.3, 11.5, 9.1–9.4) (Radwan et al. 2019; Aydin & Sevgi Birincioğlu 2022; Das et al. 2022). A study by Xu et al. (2024) reported that malaria cases rise with increasing extreme PR and flooding. FFs can force communities to relocate and exacerbate social disintegration (Radwan et al. 2019; Aydin & Sevgi Birincioğlu 2022). According to Radwan et al. (2019) and Fuso Nerini et al. (2019), large-scale movement and forced relocation are also significantly influenced by high rainfall-induced natural calamities such as FFs and landslides. This could hamper the realization of SDGTs 8.8 and 10.7. Each of these risks increases the susceptibility of the community and impedes the area's sustainable growth. Climate-resilient coping and adaptation techniques should be increased to strengthen community adaptive capacities since new CMIP6 model evidence indicates that PR extremes are predicted to grow in this century until 2100 (Deepa et al. 2024).
Figure 3

Temporal trends of the (a) ASDPR, (b) annual number of days when the PR ≥ 20 mm, (c) maximum annual 1-day PR, and (d) ASDPR > the 95th percentile. The red line in the time series (1983–2023) represents the linear regression.

Figure 3

Temporal trends of the (a) ASDPR, (b) annual number of days when the PR ≥ 20 mm, (c) maximum annual 1-day PR, and (d) ASDPR > the 95th percentile. The red line in the time series (1983–2023) represents the linear regression.

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Number of consistent dry and wet days

A dry day was considered a day when PR < 1 mm (Didi Sacré Regis et al. 2020), whereas a wet day was taken as a day where PR ≥ 1 mm. For the period 1983–2023 under study, there is a significant increase in the duration of dry spells (DSs), with a p-value of 0.033 and Sen's slope value of 0.206 (see Figure 4(a)). DSs fluctuated between 10 days (for the years 1983 and 2006) and 36 days (for the year 2018). It implies logically from this finding that the study locale occasionally experiences meteorological and agricultural droughts rather than hydrological and socio-economic droughts. Furthermore, the number of consistent wet days (CWDs) is decreasing, although at an insignificant rate with a p-value of 0.149 and Sen's slope value of −0.077 (see Figure 4(b)). The year 2010 recorded the wettest streak of 36 CWDs, while the years 2021 and 2023 had the fewest CWDs of 9 days. Additionally, the increase in both the number of consistent dry days (CDDs) and the ASDPR (see Figure 3(a)) is evidence of a heterogeneous rainfall distribution throughout the year, with a growing propensity for some days to receive above-normal rainfall. This PR erraticism eventually intensifies the vulnerability of the area to flooding hazards and landslides. Moreover, since KAKAKI districts predominantly rely on rain-fed agriculture, prolonged DSs substantially stress crops, resulting in decreased yields and crop failure, leaving most Batwa households poorer and more food insecure. It is thus crucial for smallholder farmers in the study area to be supported in adopting climate-smart agricultural practices such as affordable irrigation systems and drought-resistant crops to sustain their livelihoods in a changing climate. This would directly aid in achieving the targets of SDG 2 (Zero Hunger) and consequently SDG 1 (End Poverty) especially SDGTs 1.1–1.5, 10.1, and 10.2 (Fuso Nerini et al. 2019). A reduction in CWDs could also pose a challenge to reliable and safe water accessibility (SDGTs 6.1, 6.2, 6.4), affecting Batwa communities around KAKAKI districts. To achieve targets of SDG 6, there is an urgent need for key stakeholders in the WRH sector to implement sustainable water management practices that ensure water availability and access. Wang et al. (2023) assert that prolonged DSs can culminate in hydrological and socio-economic droughts, posing more severe repercussions. Severe droughts can cause drastic reduction in the reservoir head, which hinders sustainable operation of hydropower plants affecting consistent distribution of modern clean energy, affordably (SDGTs 7.1–7.3). Further, inconsistent provision of electricity could significantly decrease production levels of commercial enterprises, causing unemployment and reduction in economic growth (SDGTs 8.1–8.6). A study by Onyutha & Kerudong (2022) discovered that an increase in CDDs exhibited a negative correlation with the Indian Ocean polarity and Atlantic multi-decadal oscillation and a positive relationship with the quasi-biennial oscillation. Moreover, extensive duration of DSs could decrease farm-land production, causing hunger and the obliteration of jobs and wealth creation (SDGTs 1.1–1.5, 2.1–2.5, 8.1, 8.3–8.5, 12.1, and 12.2). The spread of disease-vectors may be enhanced by intensive rainfall (SDGTs 3.3 and 3.4). Additionally, scarceness of food, water, and other natural resources exacerbated by prolonged DSs could intensify disputes, endangering social justice and peace in society (SDGTs 12.1, 16.1–16.3). Drought-driven water scarcity can affect children's education, where young boys and girls are forced to spend many hours searching for water for household consumption (SDGTs 4.1, 4.2, and 4.5) (Obura et al. 2024c).
Figure 4

Temporal change of maximum annual number of (a) CDDs and (b) CWDs in the time series (1983–2023). The red line indicates the linear regression.

Figure 4

Temporal change of maximum annual number of (a) CDDs and (b) CWDs in the time series (1983–2023). The red line indicates the linear regression.

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MAM and SOND seasonal onset, cessation, length, and TPR

The MAM's onset window ranged from March 1 to March 31; its cessation window spanned from May 1 to June 30. The SOND season's onset window stretched from September 1 to September 30, and its cessation window was from November 15 to December 15. The MAM and SOND season commencement and cessation dates for the most recent 20 years of research are presented in Table 3, which was generated using R-Instat software.

Table 3

The MAM and SOND seasons' commencement and cessation dates from 2004 to 2023

YearMAM season
SOND season
OnsetCessationOnsetCessation
2004 01/03/2004 30/05/2004 08/09/2004 29/11/2004 
2005 03/03/2005 30/05/2005 05/09/2005 22/11/2005 
2006 08/03/2006 15/05/2006 01/09/2006 15/12/2006 
2007 01/03/2007 10/06/2007 05/09/2007 08/12/2007 
2008 05/03/2008 06/06/2008 NA 04/12/2008 
2009 02/03/2009 12/05/2009 25/09/2009 10/12/2009 
2010 04/03/2010 05/06/2010 06/09/2010 11/12/2010 
2011 11/03/2011 28/06/2011 03/09/2011 06/12/2011 
2012 01/03/2012 10/06/2012 02/09/2012 15/12/2012 
2013 02/03/2013 10/05/2013 10/09/2013 11/12/2013 
2014 11/03/2014 12/05/2014 05/09/2014 08/12/2014 
2015 01/03/2015 04/06/2015 01/09/2015 10/12/2015 
2016 03/03/2016 05/05/2016 15/09/2016 14/12/2016 
2017 22/03/2017 06/05/2017 02/09/2017 30/11/2017 
2018 03/03/2018 22/05/2018 03/09/2018 11/12/2018 
2019 14/03/2019 27/06/2019 01/09/2019 07/12/2019 
2020 01/03/2020 06/05/2020 25/09/2020 07/12/2020 
2021 03/03/2021 11/05/2021 01/09/2021 11/12/2021 
2022 21/03/2022 28/05/2022 05/09/2022 12/12/2022 
2023 01/03/2023 04/05/2023 09/09/2023 30/11/2023 
YearMAM season
SOND season
OnsetCessationOnsetCessation
2004 01/03/2004 30/05/2004 08/09/2004 29/11/2004 
2005 03/03/2005 30/05/2005 05/09/2005 22/11/2005 
2006 08/03/2006 15/05/2006 01/09/2006 15/12/2006 
2007 01/03/2007 10/06/2007 05/09/2007 08/12/2007 
2008 05/03/2008 06/06/2008 NA 04/12/2008 
2009 02/03/2009 12/05/2009 25/09/2009 10/12/2009 
2010 04/03/2010 05/06/2010 06/09/2010 11/12/2010 
2011 11/03/2011 28/06/2011 03/09/2011 06/12/2011 
2012 01/03/2012 10/06/2012 02/09/2012 15/12/2012 
2013 02/03/2013 10/05/2013 10/09/2013 11/12/2013 
2014 11/03/2014 12/05/2014 05/09/2014 08/12/2014 
2015 01/03/2015 04/06/2015 01/09/2015 10/12/2015 
2016 03/03/2016 05/05/2016 15/09/2016 14/12/2016 
2017 22/03/2017 06/05/2017 02/09/2017 30/11/2017 
2018 03/03/2018 22/05/2018 03/09/2018 11/12/2018 
2019 14/03/2019 27/06/2019 01/09/2019 07/12/2019 
2020 01/03/2020 06/05/2020 25/09/2020 07/12/2020 
2021 03/03/2021 11/05/2021 01/09/2021 11/12/2021 
2022 21/03/2022 28/05/2022 05/09/2022 12/12/2022 
2023 01/03/2023 04/05/2023 09/09/2023 30/11/2023 

NA = no date fitting the conditions for onset of the season.

There is considerable variability in the onset dates of each agricultural calendar year's seasons. MAM onset dates are generally continuing to occur earlier than usual thereby increasing the season's duration, as shown in Figure 5(a). These findings are consistent with research conducted by Omay et al. (2023) that focused on the Intergovernmental Authority for Development (IGAD) region of East Africa and observed a comparable trend for southwestern Uganda. However, the SOND season continues to arrive later than usual, as represented in Figure 5(b). The latest date it appeared was September 25 for the years 2000, 2009, and 2020. For the year 2008, there were no three consecutive days recorded with a total rainfall 20 mm during the SOND onset window (September 1–30). The rains arrived later in October, and thus the season lasted < 60 days. The SOND trend corresponds to the findings of Haile et al. (2020), which highlighted a notable increase over East Africa associated with deferred onset and early retreat of rain. Moreover, the SOND season is generally longer than the MAM season, with an average duration of 90 days versus 80 days. Despite this, the data indicate that the SOND season is shortening with time attributable to the late onset of the rains, while the MAM season is lengthening with time allied to the earlier onset of the rains. Early MAM seasonal onset is an agricultural advantage for the area since it extends the length of the growing season, but the shortening trend of the SOND season could interfere with the crop phenological stages, lowering yield. This annual unpredictability of seasonal onsets and cessations makes it difficult for smallholder farmers to time when to plant (Singh et al. 2023), leading to increased susceptibility to crop yield failure and food insecurity. Omay et al. (2023) asserted that although rainfall commencement and end dates and the seasonal extent are important for crop productivity and food security, they are not well documented and highlight the importance for more precise data. According to Chemura et al. (2020), understanding the spatio-temporal characteristics of seasonal lengths, onsets, and cessations in an area is imperative in planning for increased crop production, thus advancing food security. Improving CISs in the KAKAKI districts would be crucial to achieving climate-resilient agricultural productivity (Partey et al. 2018), thereby contributing to sustainable development.
Figure 5

Time series of (a) MAM onset, (b) SOND onset, (c) seasonal lengths, and (d) seasonal TPR. The straight blue line corresponds to the linear regression in the time series (1983–2023).

Figure 5

Time series of (a) MAM onset, (b) SOND onset, (c) seasonal lengths, and (d) seasonal TPR. The straight blue line corresponds to the linear regression in the time series (1983–2023).

Close modal

From 1983 to 2023, the extent of the MAM season fluctuated more than the SOND season, with ranges between 40–110 days and 73–105 days, respectively (see Figure 5(c)). The shortest MAM season (40 days) occurred in 1984, whereas that for SOND (73 days) was experienced in 2020. The year 1995 recorded the longest MAM season (110 days) from March 1 to June 19, while 2006 experienced the longest SOND season (105 days), with September 1 as the onset and December 15 as the cessation of the season. The increasing MAM seasonal variability poses a risk for climatic hazards like FFs (Ainuddin et al. 2017), which severely impact infrastructure, livelihoods, and food security. These consequently impede sustainable development. Furthermore, the results also depicted more PR inconsistency in the MAM season than in the SOND season, fluctuating between 308–655 mm and 378–623 mm, respectively. The area experiences MAM and SOND seasons' average near-normal rainfall of 404 and 531 mm, respectively. Despite this, the MAM rains were more intense, with an intensity of 135 mm/month compared to SOND's 132 mm/month. Although the MAM season for the year 1984 was the shortest (40 days), it received the highest intensity of rainfall of 253 mm/month. This can trigger climatic hazards for communities. The year 2017 recorded the lowest MAM PR totals (308 mm), whereas the year 2018 received the greatest MAM rains (655 mm). The SOND season's minimum PR totals (378 mm) occurred in 1993, while the largest amounts (623 mm) were received in 2010. Heavy PR over shorter periods exacerbate land degradation (Tofu et al. 2022), destroying terrestrial ecosystems and thus hampering the efforts to achieve SDG 15 (Life on Land) especially targets 15.1–15.6 and 15.8. These findings necessitate the urgency for sustainable land management practices to be sought to preserve ecosystems and promote sustainable agriculture in the face of a changing climate.

Time series evolution of temperature

Figure 6(a) represents the variations of annual mean DTMin. and DTMax. for the area from 1983 to 2023. Results show a significant increase (p-value = 0) in annual mean DTMin., with a positive Sen's slope value of 0.014. The annual percentage of days when DTMin. is greater than the 90th percentile is also substantially increasing. The range of annual DTMin. for the area was 13.1–14.5 °C, while that for DTMax. was 24.0–26.4 °C. The mean DTMin. and DTMax. values in the times series (1983–2023) were 13.8 and 25.1 °C, respectively. The results also revealed an insignificant (p-value = 0.135) reduction in the annual mean DTMax., with a Sen's slope value of −0.014. This explains why the DTR in Figure 6(b) is taking a significantly negative trend, with a p-value of 0.001 and Sen's slope value of −0.028. Consequently, the annual mean daily temperature is increasing at an insignificant rate with a Sen's slope value of 0.001. The results also indicated a significant decline in the monthly count of days with DTMax. > 25 °C. On average, the area experiences at least one cold wave event per year, lasting about 2 days. However, the years 1989, 1996, 1997, 2004, and 2008 had cold wave durations lasting longer than 10 days. The latest cold waves occurred in 2022, experiencing three discreet events in a single year, each lasting about 10 days. Since 2017, the area has not experienced any heat wave events. A heat wave, as defined by Perkins & Alexander (2013), is three or more days with either a positive extra heat parameter, DTMax. > the 90th percentile, or DTMin. > the 90th percentile. The latest heat wave events date back to 2016, when the area experienced six heat wave events in a single year, with a heat wave duration of 10 days and an amplitude of 31 °C as specified by the DTMax. 90th percentile. The two other years that ever experienced six discreet heat wave events include 1999 and 2005. The longest heat wave the area experienced occurred in 1991. Its duration was 37 days, with a heat wave amplitude of 31.5 °C as defined by the 90th percentile of DTMax. Temperature changes can disrupt both aquatic and terrestrial ecosystem services, thereby affecting biodiversity (Muluneh 2021; Lafia N'gobi et al. 2022). According to Fuso Nerini et al. (2019), global warming and rising ocean pH present potential dangers to aquatic environments (impacting on SDGTs 14.1–14.3 and 14.7), while ecosystems on land could drastically change through degeneration of mountaintop glaciers, augmented aridity and destruction of habitats (affecting SDGTs 15.1–15.6, 15.8). A negative impact on biodiversity lowers the natural adaptive capacity of a community against CCIs (Gebremeskel et al. 2019). This has a direct implication in thwarting efforts to achieve SDG 13 (Climate Action) and SDG 15 (Life on Land). Temperature stress also greatly contributes to water and moisture stress by increasing evapotranspiration. A study by Waqas et al. (2021) noted that temperature variations deviating away from the optimum crop temperature ranges for an extended duration have the potential to negate and ultimately lower yields. Additionally, Neild & Newman (2015) stress that different crops require a variety of temperatures throughout the entire cropping season and at different times of the day and night to attain maximum growth. In rain-fed farming, like in the KAKAKI location, the PR may not always meet the crop water requirements due to its erratic distribution and potential variations. Temperature variations can facilitate the thriving of vector-borne diseases causing catastrophic public health concerns (Tofu et al. 2022). These findings are crucial to laying climate-smart strategies for ensuring SDG 3 (Good Health and Well-being) targets are realized in the study area. Therefore, it is essential to provide farmers in Batwa communities with the necessary CISs and early-warning systems to enable rational decision-making. Failure to invest significantly in SDG 13 (climate action) could significantly affect the realization of multiple targets of the SDGs in Batwa communities. The current study established that CCIs, if not properly addressed, could directly hinder the achievement of about 77 out of the 169 SDGTs (see Table 4 and Supplementary Table S1).
Table 4

Summary of the implications of the findings interlinked with the broader sustainable development goals (SDGs) and climate resilience (The United Nations has not reviewed this table's content, and its opinions are not reflected in it)

 
 
Figure 6

Temporal patterns of (a) the annual mean DTMin. (blue line) and DTMax. (red line), and (b) the mean annual difference between DTMin. and DTMin. The red line corresponds to the linear regression in the time series (1983–2023).

Figure 6

Temporal patterns of (a) the annual mean DTMin. (blue line) and DTMax. (red line), and (b) the mean annual difference between DTMin. and DTMin. The red line corresponds to the linear regression in the time series (1983–2023).

Close modal

Implications of SDG 13 (climate action) on other SDGs

The UN member states approved the SDGs of Agenda 2030 in 2015 in a bid to address the prevalent political, socio-economic, and ecological crises confronting humanity today (Fuso Nerini et al. 2019; Obura et al. 2024a). There are 169 targets and 17 SDGs, all of which must be fulfilled by 2030 (Dadebo et al. 2023). However, the universal 2024 SDG Index approximates only about 16% of the SDGTs as being on track to realization by 2030 (Sachs et al. 2024). The other 84% depicts under-progress or even a complete setback in progress. The detrimental CCIs have impeded low-income economies' underlined ambitions to achieve all 17 SDGs. Uganda ranks 142nd with a score of 56.1%, out of the 167 countries, according to the recent UN's 2024 SDG Index findings (Sachs et al. 2024). Particularly in a complex landscape (southwestern Uganda) occupied by the Batwa inhabitants, the difficulty of timely access to CISs owing to limited financial resources, inadequate instruments and capacity for dissemination (Dinku 2019), and other factors contribute to the disintegration of information required to advance proactive actions for CCIs. Moreover, this subsection attempts to consolidate the substantial knowledge fragmentation that prevails concerning the linkage between SDG 13 and other SDGs. The practical attainment of other SDGs, encompassing clean water and energy distribution, unemployment and poverty obliteration, wealth creation and social welfare, and food availability among others, may be impacted without implementing SDG 13 (Fuso Nerini et al. 2019). Much as the SDG rankings by Sachs et al. (2024) indicated that Uganda's SDG 12 achievement is moderately increasing, the country's overall status of SDGTs is still classified as ‘limited progress’. This is because the nation still faces major challenges in maintaining the progress of SDGs 2, 3, 7, and 9. Nevertheless, SDGs 1, 5, 6, 8, 10, 11, 16, and 17 were noted as majorly stagnating while SDG13 was stagnating but with the possibility of achieving progress (Sachs et al. 2024). Although no data was available to examine the performance of SDG 4, the worst-performing ones for Uganda were SDGs 1 and 15. In the preceding subsections 3.1, 3.2, and 3.3, the implications of the findings were explicitly connected to the broader gaols of sustainable development and climate resilience. Therefore, this subsection presents a comprehensive discussion of the interaction between SDG 13 and other SDGs. It is worth stating that utilising remote sensing datasets to model CIs could advance CC early warning, awareness-creation and education (SDGT 13.3). Moreover, promoting SDG 13 (such as afforestation and re-afforestation) in Batwa community, western Uganda, can enable sustainable preservation and management of other ecological systems, including aquatic and terrestrial environments (SDGTs 6.5, 6.6, 14.1–14.7, 15.1–15.5, 15.8, and 15.9). Also, planting trees along riverbanks to control erosion might have a major positive impact on the energy sector by encouraging the efficient operation of hydropower plants, which would then distribute economical and effective clean energy (SDGTs 7.1–7.3). Consequently, the aforementioned feature would promote the rapid development of robust infrastructure, such as electric trains, sustainable small- and medium-sized businesses, and increased creativity (SDGTs 9.1–9.5 and 3.6). In addition, the upstream multipurpose reservoir formed after damming the river could enhance transportation of safe water and sanitation to the community (SDGTs 6.1–6.4). This would underpin prevention of water-associated illness, including typhoid, cholera, hepatitis, generally guaranteeing healthy living and well-being among the community (SDGTs 3.9 and 3.2–3.4). Lowering emissions associated with waste and production would guarantee achievement of multiple specific objects of sustainable consumption and production (SDGTs 12.1–12.6) (Fuso Nerini et al. 2019). In order to minimise inequality both between and within nations, SDG 13 incorporates both north–south and south–south strategies that align with pledges to eradicate emissions and promote equal opportunities between countries (SDGTs 10.1–10.4, 14.7, 15.6). Mitigating CCIs such as FFs and landslides through installing early-warning systems would enable advancement of sustainable cities and human settlements, which house a substantial proportion of humanity globally (SDGTs 11.1–11.7). Furthermore, the use of ClimPACT3, R-Instat, and remote sensing technologies should be underlined for climatology applications in higher education. Climate science, in particular, can be utilized to disseminate knowledge and expertise obtained from climate predictions (SDGTs 4.3–4.7). These initiatives can promote establishing equal, peaceful, and wealthy communities (SDGTs 16.1–16.3). Moreover, SDG 13 offers a basis for creating robust, effective, and competent institutions (SDGTs 17.1–17.19). Implementing climate-smart farming approaches such as cost-effective pressurized irrigation systems and drought-resistant crops in a complicated terrain could boost agricultural yield (SDGTs 2.1–2.5). Besides advancing welfare and employment opportunities (SDGTs 8.1, 8.2, 8.4, 8.5, 8.8, 8.9), the aforementioned attribute could subsequently alleviate poverty levels (SDGTs 1.1–1.5) (Obura et al. 2024b). Therefore, according to a detailed investigation conducted by the present study, the implementation of SDG 13 (climate action) by both developed and low-income nations could significantly contribute to the achievement of numerous SDGs targets (see Figure 7). It can be concluded that remote sensing datasets from CHIRPS and NASAPW are critical for assessing changes in CIs especially in mountainous regions with limited meteorological stations. These results from the CI analysis could provide valuable information for the health, agricultural, and water resources sectors to ensure sustainable planning and development. Further studies should be conducted to explore the synergy and/or a trade-off between each target of SDG 13 and the assessment of variations in CIs.
Figure 7

Implications of SDG 13 (climate action) on the achievement of other society-, environment-, and economy-correlated SDGs.

Figure 7

Implications of SDG 13 (climate action) on the achievement of other society-, environment-, and economy-correlated SDGs.

Close modal

The current study utilized the CHIRPS and NASAPW remote sensing data to investigate fluctuations in extreme CIs. The ClimPACT3 and R-Instat models were applied in the assessment process. The findings show that the region generally receives wetter than normal weather, with PR values from 1,006 to 1,489 mm. There was a significant (p-value < 0.05) increase in the ASDPR > the 95th percentile. Conversely, the DTMin. and DTMax. varied from 13.1 to 14.5 °C and 24.0 to 26.4 °C, respectively. These observations are particularly imperative for the agricultural, health, and water resources sectors. Furthermore, CISs would aid in the achievement of SDG 1, SDG 2, and SDG 13 targets by enhancing food security and climate resilience in Batwa farmer communities. For the reason of making well-informed decisions about water management, the participants in the hydrological and water resources sectors need information on temperature extremes, rainfall variability, and SPEI trends. In order to prepare for an epidemic of food-borne, water-borne, vector-borne, or air-borne diseases, which could help achieve SDG 3, SDG 6, and SDG 11 targets, these outputs are also critical to the health sector. In summary, even though the CHIRPS and NASAPW time series datasets have been modified to improve homogeneity, it is vital to keep in mind that certain parts of these records may still be non-homogeneous when evaluating index changes. To increase reliability, future research should think about using precise station observation data.

M.E. contributed to methodology, formal analysis, writing – original draft; W.J. contributed to data curation, writing – review and editing; and D.O. contributed to conceptualization, visualization, writing – original draft; writing – review and editing.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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