Hydro-climatic and land use/cover changes in Nasia catchment of the White Volta basin in Ghana

The Nasia catchment is the reservoir with significant surface water resources in Northern Ghana and home to numerous subsistence farmers engaged in rainfed and dry season irrigation farming. Yet, there is little understanding of the hydro-climatic and land use/cover conditions of this basin. This study investigated trends, relationships and changes in hydro-climatic variables and land use/cover in addition to implications of the observable changes in the Nasia catchment over a period of 50 years. Parameters used for the study were minimum (Tmin) and maximum temperature (Tmax), wind speed (WS), sunshine duration (S), rainfall (R), relative humidity (RH), discharge (D) and potential evapotranspiration (PET) data, 15 years of remotely sensed normalized difference vegetation index (NDVI) data and 30 years of land use/cover image data. Results show that Tmin, Tmax, WS and PET have increased significantly (p < 0.05) over time. RH and S significantly declined. R, D and NDVI have not decreased significantly (p > 0.05). A significant abrupt change in almost all hydro-climatic variables started in the 1980s, a period that coincides with the occurrence of drought events in the region, except WS in 2001, R in 1968 and D in 1975, respectively. Also, D showed a positive significant correlation with RH, R and PET, but an insignificant positive relationship with S. D also showed a negative insignificant correlation with Tmin, Tmax and WS. Areas covered with shrubland and settlement/bare lands have increased to the disadvantage of cropland, forest, grassland and water bodies. It was concluded that climate change impact is quite noticeable in the basin, indicating water scarcity and possibilities of droughts. The analysis performed herein is a vital foundation for further studies to simulate and predict the effect of climate change on the water resources, agriculture and livelihoods in the Nasia catchment.


Introduction
Climate change presents the most pressing challenge of the twenty-first century, with extraordinary impact on natural ecosystems, economic sectors, society and water resources (Arnell 2004;Khaliq et al. 2009;Sabbaghi et al. 2020;de Hipt et al. 2018;Schilling et al. 2020;Baarsch et al. 2020). Climate change is unequivocal, manifested by rapid warming of the globe and increasing the frequency of extreme events, such as floods and droughts (IPCC 2014). Africa, for example, is expected to experience negative climate change impacts, contributing to already present problems of widespread poverty and low development (World Bank 2010; Mikulewicz and Taylor 2020). At the background of climate change is the variability of the hydro-climatic parameters, such as temperature, rainfall, relative humidity, discharge, potential evapotranspiration and radiation, both in their long-term average and by an increase over time. The already high temperatures and largely erratic rainfall are expected to increase in sub-Saharan Africa over the twenty-first century (Speranza 2010;IPCC 2014;Serdeczny et al. 2017;Codjoe and Atiglo 2020).
Variations in climatic conditions are important determinants of vegetation growth and density across the world and, especially, in tropical and subtropical Africa (Warburton et al. 2012;Schmidt et al. 2014). Also, feedbacks from land surface processes and vegetation dynamics influence local and regional climate variability (Wang and Eltahir 2000), especially in West Africa and the Sahel Zone (Long et al. 2000;Nicholson et al. 2000;Los et al. 2006;Paeth et al. 2009). Changes in land cover, particularly vegetation, are likely to aggravate the climate change situation in a way that the hydrological cycle will be altered, resulting in an increase in frequency and severity of droughts and floods which in turn influences agriculture, water supply, environmental sustainability and protection from floods (Aduah et al. 2018). The combined effects of climate variability, land use/cover changes and unsustainable water management practices have led to a significant alteration in the water balance of the river basins (Buma et al. 2016). Land use/cover changes are caused by population pressure as well as expansion of agricultural lands through unplanned and inappropriate land management practices to meet the food demands of a rapidly growing population. Unsustainable land use/cover activities, therefore, affect soil structure, texture and fertility that play a key role in food production (Lal et al. 2015).
Analysing the direction and magnitude of the variation in the hydro-climatic variables is important for understanding climate change and providing a basis for determining future scenarios of climate impact (Chaouche et al. 2010;Reiter et al. 2012;Unal et al. 2012;Asfaw et al. 2018;Meshram et al. 2020). Detecting the historical trend of vegetation, often expressed in normalized difference vegetation index (NDVI) and land use/cover changes, particularly improves our understanding of the changing planet and provides a clue about the productivity of lands (Tian et al. 2015;Gichenje and Godinho 2018;Frédérique et al. 2019;Rezende et al. 2020). Trend analysis of hydro-climatic variables and vegetation is particularly relevant for water resource decisionmakers as they prepare to deal with the possible effects of climate variability and change on water availability (Sahoo and Smith 2009;Oguntunde et al. 2006;Zhou et al., 2015a, b;Tehrani et al. 2019).
Many regions of the world are increasingly facing a decline in freshwater resources, due to both natural and manmade causes. Climate and land use/cover change are likely to aggravate this situation in a way that the hydrological cycle will be intensified resulting in an increase in frequency and severity of droughts and floods which influences agriculture, water supply, environmental sustainability and protection from floods and infrastructure (Aduah et al. 2018). Depending on the severity, water deficits can result in catastrophic consequences (Amisigo, 2006).
The availability of freshwater in sub-Saharan Africa is fundamental to economic growth and social development (Kankam-Yeboah et al., 2013). In the Volta basin of West Africa, where Ghana is situated, there are competing demands for water use both within and among the riparian countries of the basin. This is manifested in the numerous dams and reservoirs constructed throughout the basin for various purposes including industrial, agricultural and domestic water supplies (Amisigo, 2006).
The Ghana Water Research Institute of the Council for Scientific and Industrial Research (CSIR-WRI) reports that all river basins in Ghana will be vulnerable and the whole country will face acute water shortage by the year 2020 (Kankam-Yeboah et al., 2011). It also reported a general reduction in annual river flows in Ghana by 15-20% for the year 2020 and 30-40% for the year 2050, due to an increased irrigation water demand of 40-150% for 2020 and 150-1200% for 2050 (Kankam-Yeboah et al., 2011). According to Abdul-Ganiyu et al. (2011), the main surface water resources in Northern Ghana are concentrated in the White Volta and the Nasia River systems, which flows only 3 or 4 months during the year, causing seasonal deficits across the region. This poses serious problems for traditional rainfed agriculture, especially as food demand grows, thus slowing down rural development. Also, the authors mention that the seasonal shortage of water affects irrigation during the dry season for the Nasia Irrigation Project, which operates as a run-of-river scheme for all year-round crop production. The predominant land use is arable food production and widespread grazing of large numbers of cattle and other livestock. Plinthic ferralsols (groundwater laterites) and Eutric nitosols (savannah ochrosols) with their intergrades are the predominant soil types in this region (Addai et al., 2016).
Given the above situation and pressing issues, understanding the hydro-climatic variability and land use/cover changes in the Nasia River catchment is important in Northern Ghana, because the availability of water resources is a significant factor in this highly productive agricultural region. While the causes and the mechanisms of these changes are a matter for other studies, the relevant question for this case is how has climate change affected the trends of these hydro-climatic variables? Therefore, the objective of this study was to determine the historical trends in selected hydro-climatic variables (minimum and maximum temperature, wind speed, sunshine duration, rainfall, relative humidity, discharge and potential evapotranspiration), NDVI and land use cover/change in Nasia sub-basin of the White Volta and to establish the relationship between these parameters and discuss the possible implications of the observable changes in the Nasia catchment to agriculture in the region.

The Nasia River catchment
The Nasia River (Fig. 1) is a tributary of the White Volta in the Northern Region of Ghana, with a catchment area of about 5,400 km 2 and a mean annual runoff of 550 million m 3 (WRCG 2008). It is geographically positioned between latitudes 9° 55′ and 10° 40′ N and longitudes 1° 05′ W and 0° 15′ E (Adu, 1995). The area is characterized by unimodal rainfall, with an annual average between 1000 and 1300 mm, which peaks between late August and early September (Elikplim et al., 2018). Temperatures in this region are consistently high. The hottest months in the year are March and April, just before the beginning of the rainy season, while the coolest months are July and August. The average maximum and minimum temperatures of 34 °C and 23 °C, respectively, are recorded in the basin (Abdul-Ganiyu et al. 2011). The floodplain soils vary in texture, from very fine sands to heavy clays, and are developed over levees, old river beds, sloughs and low river terraces. Most of the Nasia catchment is very gently undulating. It has broad, poorly drained valleys and extensive floodplains adjacent to the Volta and Nasia rivers, where altitudes vary between 108 and 138 m above mean sea level (Abdul-Ganiyu et al. 2011). It has a relatively short rainy period, stretching from May to October, with estimated reference evapotranspiration (ETo) above 1600 mm/annum (Kranjac-Berisavljevic, 1999). The remaining months of the year are very dry, posing challenges to domestic and agricultural activities, due to water unavailability in the basin. The people of the area are engaged in subsistence agriculture mainly on "compound farms" which lie immediately around the houses and "bush farms", which may border on the compound farm or are located several kilometres away from the main communities. Rice, maize, legumes and vegetables are cultivated in the rainy season, while tomatoes and onions are cultivated in the dry season under irrigation. Many householders rear sheep and goats, as well as chickens and guinea fowls, but few others keep cattle. The animals are kept for security reasons or as a capital investment (Abdul-Ganiyu et al. 2011).

Data collection and quality assurance
This study utilized climate, hydrological and land use/ cover (LULC) data (Table 1). Fifty years of daily hydroclimatological data were collected from relevant government institutions. The hydrological data, i.e. river discharge, was obtained from the Ghana Hydrological Services Department (HSD), while the climatic data, i.e. rainfall, minimum temperature and maximum temperature, relative humidity, wind speed and sunshine, were collected from Ghana Meteorological Agency (GMET) for the Tamale synoptic station. Also, annual NDVI data was collected from NASA Giovanni website. Derived from red and near-infrared band reflectance, NDVI is an efficient indicator for vegetation monitoring due to its simplicity and close relation to vegetation productivity (Tian et al. 2015). NDVI provides information about the quantity of vegetation present in a given area and its state of health or vigour of growth thus a good indicator for degradation (Meneses-Tovar 2011). More than 20 vegetation indices have been proposed and used at present, yet NDVI has been widely used with its values ranging from − 1.0 to 1.0, where higher values are for green vegetation and low values for other common surface materials such as bare soil represented with NDVI values close to 0 and water bodies having negative NDVI values (Jasinski 1990;Sader and Winne 1992;Lillesand et al. 2004;Sesnie et al. 2008).
LULC maps of 2000 and 2010 were obtained from the GlobeLand30 map generated by the Chinese Government and the 2020 LULC map generated from Landsat 8 image acquired from the US Geological Survey GLOVIS website.

Analysis of hydroclimate and NDVI variables
The hydro-climatic and NDVI data were analysed using the R statistical software. The datasets were first separately analysed to determine trends and subsequently together to describe the relationship between the variables. The analysis generally followed three main steps. First, analysis of basic statistical properties of the variables was determined using the mean, median, mode, skewness and kurtosis, variance and standard deviation.
Secondly, the Mann-Kendall trend test (Mann 1945), a non-parametric method, was used to investigate the trends in annual rainfall (mm), annual discharge (m 3 s −1 ), relative humidity (%) and minimum and maximum temperature (°C), wind speed (km/day), sunshine (h) and NDVI data. The presence of a breakpoint in the time series of annual averages of the variables was examined using the non-parametric test of Pettitt (Pettitt, 1979). Pettitt's test allows the detection of abrupt changes, whether artificial or natural, in the mean of the time series (Mallakpour and Villarini 2016).
The null hypothesis was tested at a 95% confidence level (α = 0.05) for all the variables. The Mann-Kendall trend test was selected because it accommodates missing data and outliers and does not require the data to be normally distributed (Partal and Kahya, 2006). At the same time, it has low sensitivity to abrupt breaks due to inhomogeneous time series (Tabari and Talaee 2011). This test has been extensively and successfully used to detect trends in hydro-climatic studies (Xu et al. 2010;Sun et al. 2013;Zhang et al. 2015;Mwangi et al. 2016) and NDVI (Forkel et al. 2013;Osunmadewa et al. 2014).
The null hypothesis H0 assumes that there is no significant trend (the data is independent and randomly ordered) and this is tested against the alternative hypothesis H1, which assumes that there is a significant trend (Önöz and Bayazit 2012). The test statistic Zs is used as a measure of the significance of the trend. This test statistic is used to test the null hypothesis, H0. Kendall's tau was used to measure the strength of the trend. In addition to the Mann-Kendall test, the results in linear trend lines were compared and plotted for each variable. The Mann-Kendall test statistic (S) is given as follows (Gocic and Trajkovic 2013;Kambombe 2018): where When S is greater than 0, it implies a positive trend, and a negative S indicates a decreasing trend. The S is approximately normally distributed for n ≥ 8, with the variance given as: In case of tied ranks in the data, the statistic Zs = 0 and variance of S, Var(S) is calculated by: where q is the number of tied groups and t p is the number of data values in the P th group. The standardized Z value is used to determine the significance of any trend in the data set. The null hypothesis stating that there is no trend in the dataset is rejected | Z c | or > Z 1− ∕2 or if the p-value is less than the level of significance (p < α = 0.05). Sen's slope technique estimates the magnitude of monotonic trends in N pairs of data which was used in this study (Hirsch et al. 1982). A monotonic upward or downward trend for a variable implies that there is a consistent increase or decrease in the variable through time, but the trend may or may not be linear (Hirsch et al. 1982). Sen's slope is given as: in which Qi is Sen's slope while x j and x k are data values in years j and i, where 1 < j < i < n. A positive Q i value indicates an upward trend, while a negative value indicates a downward trend.
Thirdly, Pearson's correlation analysis was used to determine the relationship between the variables. (3) (4) in QGIS under the Semi-Automatic Classification Plugin (SCP). The random forest algorithm machine learning was used to classify the image in R software (Thanh Noi and Kappas 2018). The 2016 European Space Agency (ESA) Climate Change Initiative (CCI) S2 prototype land cover map at 20 m of Africa was acquired from ESA and combined with Google Earth image of 2020, and observation or knowledge of the basin were references used for the classification (Forkuo and Frimpong, 2012). Both pixel-based and areabased error matrix was done to assess the accuracy of the classification (Olofsson et al., 2013). The overall accuracy of the 2000 and 2010 GlobeLand30 is 78.6% and 80.33% respectively, which was validated by over 150,000 points in 80 out of 853 tiles for the 2010 land cover map (Chen et al. 2015). The overall accuracy for the 2020 LULC maps was 90.53% and 77.15% for the pixelbased and area-based error matrix assessment respectively (see Tables 5 and 6 in Appendix for details of the pixelbased and area-based error matrix for 2020).

Results
In this section, the findings of the analysis are presented in three main ways. Firstly, the descriptive statistics of the 8 variables (climate, hydrological and NDVI data) are shown. Secondly, the results of the trends in the variables are also presented. Thirdly, the relationship between these variables and how they influence river discharge was established using a multivariate regression model.

Temporal characteristics of the variables in Nasia catchment
Over 50 years , the Nasia catchment received an annual total rainfall (R) ranging from 695 to 1666 mm, with a mean value of 1093 mm. Discharge (D) of the Nasia River ranged from as low as 7.83 to 20,757.3 m 3 /s with a mean flow of 6931.6 m 3 /s. Also, within the 50 years, the catchment recorded an average minimum (Tmin) and maximum (Tmax) temperature of 22.6 °C and 34.1 °C respectively, the average sunshine (Sun) in hours per day of 7.3, with relative humidity (RH) of 57.98%. The average wind speed (WS) over 50 years is 3.25 kt. Also, the average NDVI for the 16 years is 0.47. Table 2 provides descriptive statistics of the selected variables.

Annual trends in the selected variables
The observed slope for D, R, S, RH and NDVI was negative, indicating a decreasing trend, while Tmin, Tmax, WS and PET showed an increasing trend. The decreasing trend in R and D was insignificant (p > 0.05) at a rate of − 0.086 mm/

Image processing and land use land cover mapping
The LULC maps of 2000 and 2010 were extracted from the GlobeLand30 maps produced by the Chinese Government (global land cover map at a spatial resolution of 30 m) (Jun et al. 2014). Two scenes of the GlobeLand30 dataset covering Ghana, that is, N30_05 and N30_10, were mosaicked since the basin fell within both scenes. The 2020 map classification was performed by the authors. The classes in the 2000 and 2010 maps were adopted for the 2020 classification, i.e. cropland, forest, grassland, shrubland, water bodies and settlement/bare areas. Bare areas were combined with settlement due to the dryness of the basin located in the Guinea Savannah zones. Moreover, most of the settlements are farming communities with less reflective roofs (thatch roofs) to depict settlement. Landsat 8 images at 30 m spatial resolution and cloud cover criterion of less than 10% acquired on 26 February 2020 from path 194 row 53 were acquired freely from the United States Geological Survey's (USGS) GLOVIS. Atmospheric correction for temporal analysis was done year and − 35.485 m 3 /year, respectively. S, RH and NDVI were, however, significant (p < 0.05) at a rate of − 0.007 h/ day/year, − 0.084% and − 0.002, respectively. A significant (p < 0.05) increasing trend was observed for the remaining variables (Tmin (0.022 °C), Tmax (0.028 °C) and PET (4.233 mm)) except for WS which increased at an insignificant rate of 0.008 kt.
R recorded an earlier but insignificant change in mean value in the year 1968, which was consistently followed by an insignificant change in D in 1975. Tmax and S observed abrupt changes in the years 1980 and 1981, respectively. Also, a close breakpoint in Tmin and PET was identified in the years 1986 and 1987, respectively. WS and NDVI recorded a breakpoint in the years 2001 and 2014, respectively. Results of the trend and breakpoint year estimates are presented in Table 3. Annual time series, anomalies and correlations for all variables are shown in Figs. 2, 3, and 4 respectively.

Relationship of the hydro-climatic variables
Results show that rainfall contributes significantly to relative humidity and discharge throughout the year, showing a positive relationship. Rainfall also has a positive but insignificant relationship with potential evapotranspiration and sunshine and an insignificant negative correlation with wind speed and minimum and maximum temperatures. Potential evapotranspiration has a significant positive relationship with minimum temperature, relative humidity and discharge but insignificantly increases with maximum temperature, sunshine and rainfall. Potential evapotranspiration also

Fig. 3
Inter-annual anomalies of the hydro-climatic and NDVI variables: total discharge (m 3 /s); sunshine (h/days); maximum temperature (°C); wind speed (Km/h); relative humidity (%); mean minimum temperature (°C); rainfall (mm); PET, potential evapotranspiration (mm); and NDVI, normalized difference vegetation index) (Authors' design, 2020) has an insignificant negative relationship with wind speed. When both minimum and maximum temperature increase, discharge, duration of sunshine, relative humidity and rainfall insignificantly decrease, meanwhile wind speed increased but insignificantly. Both maximum and minimum temperatures have a significantly positive relationship.

Land use/cover changes over the last 3 decades
The landscape dynamics over 30 years in the Nasia catchment was assessed from 2000 to 2020 at decadal intervals (interval 1 (2000-2010) and interval 2 (2010-2020)) ( Fig. 5). Table 4 presents the land use/cover class sizes in percentage and their changes during the two intervals.
The total land area of the Nasia catchment is 534,252 hectares. From 2000 to 2010, water bodies decreased by 0.34% and increased by 0.10% from 2010 to 2020. Forest coverage also decreased by 9.69% during the first interval and increased by 4.23% in the second interval.
Grassland and shrubland increased by about 5.05% and 10.46%, respectively, in the first interval. During the second interval, grassland decreased at 14.76%, while shrubland again increased by 7.17%. Settlement/bare areas increased in both intervals with a higher increase from 2010 to 2020 (3.04%). Cropland decreased by 5.55% in the first interval and marginally increased (0.22%) in the second interval. Over the entire 30-year period, shrubland and settlement/ bare lands have increased by 17.62% and 3.1%, respectively,   (Fig. 6).

Discussion
This paper sets out to understand the trends and relationship between the hydro-climatic variables and land use/ cover changes in the Nasia catchment. Here, we discussed the implications of the results, and their impacts on agriculture and the livelihood of the people in the catchment are discussed.

Maximum and minimum temperature and rainfall
The occurrence of a significant increasing trend in both maximum and minimum temperature over the study area highlights the existence of a warming climate in the Nasia catchment in the Northern region of Ghana. Rainfall within the basin shows a decreasing but insignificant trend. Similar trends of temperature and rainfall have been discussed in studies performed in Northern Ghana, where Nasia catchment is located (Amikuzino and Donkoh 2012;Frimpong et al. 2014;Issahaku et al. 2016;Nyadzi 2016;Awuni et al. 2018). Rainfall variability over West Africa is naturally high, with studies showing rainfall shortage of about 10-15% during the 1980s, relative to the 1950s (Mahe 2006). At the same time, temperature increased over Africa, with significant changes since the late 1970s (Hulme et al. 2001). The negative impact of increasing temperatures (minimum and maximum) and decreasing rainfall has implications for soil and water management and agriculture productivity in general. An increase in temperature coupled with warm nights and reduced rainfall will in particular affect crops and weed growth and also increase the prevalence of insects, pests and diseases (Hatfield et al. 2011).

Sunshine hours
The duration of sunshine (hours) within the basin has significantly declined, perhaps due to increasing atmospheric aerosols and other air pollutants (Stanhill and Cohen 2001), and increased cloudiness (Cutforth and Judiesch (2007). Sunshine duration remains an important climatic factor driving crop productivity especially because it drives photosynthesis which greatly influences plant growth (Wu et al. 2006;Alemu and Henebry 2017). Agronomic studies have shown that sunshine plays a critical role in crop water demand (Baskerville and Emin 1969;Ritchie and Nesmith 1991). In a study conducted by Guo et al. (2020), the authors found that the impact of sunshine duration on agricultural water use is statistically significant and that a 1% increment of sunshine duration hours will partially lead to a 0.145% decrement in agricultural water use. Stanhill and Cohen (2001) also report that a decrease in solar radiation would impact crop water balance and evapotranspiration of crops with a limiting effect on crop productivity.

Potential evapotranspiration
The findings show that potential evapotranspiration in the Nasia basin has significantly increased over the last 50 years. This implies that open water evaporation, bare soil evaporation, rainfall interception evaporation and vegetation transpiration could also be increasing within the basin (Zeng et al. 2018;Tadese et al. 2020). Potential evapotranspiration is an important constituent of the energy and hydrological cycles at the land surface and a vital regulating factor for agricultural water management and calculating crop water requirements (Pengli et al. 2006;Paparrizos et al. 2017;Han et al. 2018). Apart from sunshine duration as mentioned earlier, the significantly increasing wind speed and temperatures and decreasing in relative humidity at a significant rate might have contributed to the rapid increase in potential evapotranspiration which could impact ecological changes, the hydrological cycle and agriculture irrigation management in the basin (King et al. 2015;Ning et al. 2016).

Wind speed and relative humidity
The increase in wind speed and decrease in relative humidity will not only affect agriculture in the basin but also have harmful impacts on the health of the inhabitants (Csavina et al., 2014), and when breathed, this can have negative impacts on the human respiratory and cardiovascular systems, due to the spores and contaminants associated with dust and aerosols (Ghio and Devlin 2001;Low et al. 2006;Quintero et al. 2010;Csavina et al. 2011;Degobbi et al. 2011). The combination of wind speed and relative humidity could increase the presence of dust and aerosols in the basin. Wind speed remains the primary factor in dust generation with soil structure and vegetation cover also playing significant roles (Zobeck and Fryrear 1986;Zobeck 1991;Yin et al. 2007). Also, the threshold velocity for aeolian erosion is dependent on relative humidity due to its impact on soil surface moisture content which, in turn, affects interparticle cohesion (Ravi and D'Odorico 2005;Ravi et al. 2006;Neuman and Sanderson 2008). Already, the North of Ghana is known to be very dusty, as a result of local and regional aeolian erosion due to the nature of the soil materials dominated by the clay mineral kaolinite (Tiessen et al. 1991;He et al. 2007). The concentration of dust and aerosols in the air gets worst during the harmattan where the dry dust-laden continental wind from the Bodélé Depression in the Chad basin blows over the West African countries along the Gulf of Guinea (Sunnu et al. 2008;Lyngsie et al. 2011).

River discharge
The insignificant decrease in annual discharge of the Nasia River with the corresponding insignificant decrease in rainfall and significant rising temperatures and evapotranspiration is indicating water scarcity and possibilities of droughts in the basin (Sheffield and Wood 2008;Dai 2011;Seneviratne 2012). Some studies have shown that for almost all the rivers of West Africa, discharge has decreased after 1970. Yet the changes in the rainfall and discharge relationships are not proportional, presenting a paradoxical situation (Mahé et al. 2000;Mahe 2006). The decreasing trend in the discharge of the Nasia River is bad news for inhabitants of the basin who depend on its water for both agriculture (irrigation) and domestic use. The water crisis in the basin will significantly impact the livelihood of people as rainfed agriculture remains the main economic activity challenged by a long period of dry season. Abdul-Ganiyu et al. (2011) however mention that the flow of the Nasia River may not be attributed to climatic factors alone but also influenced by the physical characteristics (such as topography, soil and vegetation) as well as human activities in the catchment. Adeyeri et al. (2020) however reported that the contribution of human activity to annual discharge variation can be remarkably larger than the contribution of rainfall variability in several regions of the world.

Hydro-climatic jumps and implication for agriculture in Nasia
Following the beginning of R reduction in 1968 and subsequently discharge in 1975, a significant breakpoint of Tmin, Tmax, S, RH and PET occurred within the 1980s a period that coincides with the occurrence of unprecedented drought events in the history of Ghana (Tan and Rockmore 2019). The drought of 1968The drought of -1983 in West Africa, which started imperceptibly in the 1960s in the Sahel-Sahara-Sudano-Guinea region, affected all meteorological stations in Ghana. The North of Ghana particularly recorded a long and pronounced drought years resulting in the destruction of farms, livestock and other forms of life and property by bush fires (Tandoh, 1985). Since the analysis reveals a breaking point and trends that coincide with past events, the reduction in R and D, in particular, has significant implications for agriculture in the area. Water availability is becoming a limiting factor for crop production.
Planting drought-resistant crop varieties with low water requirements in addition to sustainable water management practices is a possible way to increase yields. Moreover, agriculture in the Nasia catchment is generally hindered by low soil quality which has limited the production of crops to mainly maize, sorghum and millet, which require relatively high levels of water during their growth periods (Antwi-Agyei et al. 2012).

Trend and implication of land use/cover change in Nasia
Over the last three decades, land use/cover are changing in the Nasia catchment; shrubland and settlement/bare lands have increased, while cropland, forest, grassland and water bodies have decreased. The land use/cover changes can allude to the changing hydro-climatic pattern, population growth and economic activities in the basin (Akpoti et al. 2016;Awotwi et al. 2018). The relationship between land use/cover changes and river discharge depends on the basin's size and location, elevation, land management and LULC types (Li et al. 2001). While this study could not establish the relationship between hydro-climatic variables and land use/cover changes, NDVI observed a similar declining trend as rainfall, river discharge, potential evapotranspiration, relative humidity and sunshine duration. Similarly, forests, water bodies, cropland and grassland also declined. Hao et al. (2004) concluded that a positive correlation exists between river discharge and forest cover over the Naoli Basin of China.
It is, therefore, speculated that the trend in hydro-climatic conditions of Nasia catchment in addition to human activities such as settlement development, agriculture and deforestation plays a critical role in the land use/cover pattern of the area. Human impact on the environment is increasing the speed of land cover changes in the area. Generally, in Africa, people practice deforestation to increase croplands (Mahe 2006). Yet in this study, deforestation resulted in increased settlement and shrubland coverage, compared to croplands, signalling a reduction in farming activities in the basin. Excessive use of trees for charcoal and wood fires and uncontrolled bushfires are the main drivers of deforestation in sub-Saharan Africa (Obahoundje et al., 2018). Firewood or wood fuel accounts for 70% of sub-Saharan Africa total energy production, and due to the increase in population growth rate, and relative price changes of alternate energy sources for cooking, it is expected that the trend of using firewood will continue (Kebede et al., 2010).

Limitations and relevance of the study
Climate variability could be a natural expression of atmospheric dynamics, yet temporary discontinuities in the data produced by non-climatic factors such as location of weather station, changes observation routine, recalibration or degradation of sensors are also possible (Wijngaard et al., 2003). It is recognized that the major setback of the study is the inability to use robust methods to determine the impact of the changing hydro-climatic factors and land use/cover changes on agriculture and livelihood as a whole. However, the speculations made in the discussions are based on relevant existing literature. Also, another weakness of the study was that the hydro-climatic data used may not reflect the current trend of events as they ranged from 1961 to 2010. However, the lack of data did not adversely affect the results obtained from this study. Therefore, further study to examine the current and future trends as well as to establish the impact on agriculture and livelihood using impact models is recommended. Assessing the long-term behaviour and relationship and detecting breakpoints of hydro-climatic factors and land use/ cover are important, not only to increase knowledge about climate variability but also to develop strategies and implement more adequate water management policies at regional and local scales for the planning of sustainable agricultural practices (de Carvalho et al. 2014;Huntington 2010).

Conclusion and recommendations
This study examined the trends of hydro-climatic variables (minimum and maximum temperature, wind speed, sunshine duration, rainfall, relative humidity, discharge and potential evapotranspiration), NDVI and land use cover/change in the Nasia catchment. The relationship between these parameters was also analysed in addition to the possible implications of the observable changes in the Nasia catchment.
Generally, the results presented signal water scarcity and possibilities of droughts in the Nasia catchment. The impact of climate change on the overall hydro-climatic variables is quite noticeable. At a 95% confidence level, minimum and maximum temperatures, wind speed and potential evapotranspiration showed a significant upward trend. Relative humidity and sunshine duration showed a significant downward trend. Rainfall, river discharge and NDVI also showed a downward but insignificant trend. Almost all the trends in hydro-climatic variables started in the 1980s, except wind speed in 2001, rainfall in 1968 and discharge in 1975. Discharge showed a positive significant correlation with relative humidity, rainfall and potential evapotranspiration, but an insignificant positive relationship with sunshine duration. The discharge also showed a negative insignificant correlation with temperature (minimum and maximum) and wind speed. Finally, over the entire 30-year period, shrubland and settlement/bare have increased to the disadvantage of cropland, forest, grassland and water bodies.
The limitation of this paper resides in the fact that the combined effect of the understudied variables on water resources, agriculture and livelihood of the inhabitants was speculated, based on literature. Also, the lack of data could not allow current analysis. However, the findings of this paper could help researchers understand the annual variability of hydro-climatic variables and land use/cover changes in the Nasia catchment and therefore become a foundation for further studies. There is a need for additional research to incorporate hydro-climatic variables, land use/cover and human activities into empirical models to identify specific cause and effect relationships, particularly on river discharge. Once these relationships are determined, impact models could be used to simulate and predict the effect of climate change on the water resources, agriculture and livelihood in the Nasia catchment.

Table 5
Accuracy of generated land use/cover map (pixel-based error matrix) for 2020