Abstract
Soil management decisions should consider physical potential of the environment, weather variability, and requirements of crops to maximize production to the potential limits. This calls for characterization of environments using selected input variables. Such studies are scanty in southern central Rift Valley of Ethiopia due to which the area is considered homogeneous and identical for agricultural planning, extension, and input delivery programs. Thus, to investigate the scenario, we employed principal component, clustering, and GIS analysis on geo-referenced physiographic and climatic attributes, and their statistical variables obtained from 43 stations with the objective of identifying homogeneous management units with similar physiography, weather pattern, and production scheduling. The analysis of principal components (PCs) indicated that three PCs explained 74.7% of variance in October, November, December, and January (ONDJ), four PCs explained 79.3% of variance in February, March, April, and May, and four PCs explained 80.5% of variance in June, July, August, and September (JJAS). Cluster-I was characterized by high altitude and low temperature in ONDJ season. Cluster-II was characterized by low altitude and high temperature across most seasons. Cluster-III was intermediate in altitude, temperature, and rainfall. Cluster-IV was characterized by high rainfall in JJAS. In all the clusters, PC1 was the mean rainfall component with strong association with altitude and longitude, while PC2 was the temperature component. PC3 is the statistical component with strong influence from mean rainfall. Thus the factors that determine the formation of clusters are reduced from 12 to 5 (T mean, latitude, longitude, altitude, and RFmean) and 43 stations are grouped into 4 clusters (Shamana, Bilate, Hawassa, and Dilla) which are geographically and ecologically distinct. These clusters require different sets of agro-meteorology advisory, maize management, and input delivery strategies.
Nomenclature
- ANOVA
-
analysis of variance
- ArcGIS
-
geospatial software to view, edit, manage, and analyze geographic data
- CV
-
coefficient of variability
- Eigen value
-
coefficients of linear transformation that measure the magnitude of variability
- Eigen vector
-
directions along which linear transformation acts, stretching or compressing input vectors
- FMAM
-
February, March, April, and May
- GIS
-
geographic information SYSTEMS
- ITCZ
-
inter-tropical convergence zone
- JJAS
-
June, July, August, and September
- L-moments
-
a sequence of statistics used to summarize the shape of a probability distribution
- ONDJ
-
October, November, December, and January
- PC
-
principal components obtained from PCA
- PCA
-
principal component analysis
- RFmax
-
maximum monthly total rainfall
- RFmean
-
mean monthly total rainfall
- RFmin
-
minimum monthly total rainfall
- STDEV
-
standard deviation
- T max
-
maximum monthly temperature
- T mean
-
mean monthly temperature
- T min
-
minimum monthly temperature
1 Introduction
Maize is a strategic crop for the achievement of food security in Ethiopia, which grows in varying eco-climates ranging from moisture stress areas to high rainfall areas and from lowlands to the highlands [1]. The crop requires over 500 mm of precipitation per season [2]; however, this much rainfall was not available in the growing season in rain-fed farming systems. This makes the crop prone to shocks related to climate variability and change in rain-fed farming conditions. In dry sub-humid and semiarid areas, the productivity of maize ranged between 1 and 300 MT/ha [3,4]. When rainfall was sufficient, average of 3–4 tons per hectare bumper harvest was recorded leading to 20% and over increase in the maize yield whereas in years with 10% decrement in rainfall maize production was reduced by about 23% and more [5].
Rainfall is the single most important source of water for maize production in south central production zones of Ethiopia [6], whose variation could be explained by global and local factors. March to May surface temperature of the equatorial Pacific, mid-latitude northwest Pacific, Indian, Red sea, and Atlantic oceans exert an influence on the June, July, August and September (JJAS) rains with strong correlation coefficient as prominent global factor [7–10]. The rains during JJAS are due to ElNino Southern Oscillation (ENSO) that causes north ward advance of inter-tropical convergence zone (ITCZ) and easterly jets producing rains in the majority regions of the country [8]. Moreover, November to December sea surface temperature of northern Atlantic and Indian Oceans showed strong correlation coefficient with February, March, April, and May (FMAM) rains for the study area [7,11,12]. The rains during FMAM are due to ENSO that causes northward advance of the ITCZ and westerly jets which produces rains in the east, southeast, and southern parts [7,8]. As wet air rises, expands, and cools (due to mountains and hills), it will reach its dew point where condensation occurs and forms a cloud. When condensed water particles merge and become large, it will fall as rain on windward side [11]. The rain shadow on leeward side becomes evident causing variation in timing, amount, and distribution of rainfall [11]. Although Sea surface temperature predictions are similar, the areas represent varying topography, climatic pattern, and potential for maize production [13,14]. Moreover topographic variability associated with altitudinal and longitudinal differences show spatial rainfall complexities at local (smaller) scale [15,16].
One way of learning and understanding the variability and complexity posed by terrain with orographic effect involves clustering and mapping [17,18]. Area clustering is important to reduce the extensive data requirements for water resource management, agricultural planning, agro-climatic regionalization, and the assessment of regional development [19]. Using location specific agro-climate information, Zhou and his colleagues carried out clustering study in small area of land (150,000 ha) in Murrumbidgee Irrigation Area of Australia and found 3–7 clusters employing rainfall, temperature, growing degree days, humidity, and evapotranspiration variables [20]. Similarly, a 60 ha rain-fed wheat field was clustered into 2, 3, and 4 zones requiring alternative site specific management using variables like electrical conductivity, elevation, soil depth, soil organic matter, clay, and yield in Argentine Pampas [21]. Jaynes and his colleagues considered yield data of 5 years collected from 224 plots in association with elevation, soil electrical conductivity, growing season rainfall amount, and applied cluster analyses to develop potential management zones of similar yield patterns with prediction precision of 80% [22]. Some authors included L-moments of rainfall along with latitude, longitude, and altitude to define homogeneous regions [23,24].
Although different methods for choosing input variables for environmental characterization exist, principal component analysis (PCA) and clustering were used simultaneously to identify important attributes and superior clusters in biological sciences [25–28]. Both techniques have also been used to delineate a relatively homogenous region by authors including Kar et al. [29], Oliveira-Júnior et al. [30], and Haque and deSouza [31] who adopted it to generate the (PCs) consisting of different physical, hydrological, and meteorological variables. Bisetegne et al. [32] retained four eigen values associated with specific eigen vectors to explain 75% of the variance of 24 gauge stations and create five clusters using PCA technique in Ethiopia. Later, Eklundh and Pilesjö [33] divided Ethiopia into seven regions using PCA technique. Similarly various studies were carried out in Ethiopia over years and rendered different clustering results [9,10,12,34]. The variations in clustering results were attributed to difference in the base period and purpose of the study. However, these studies were not linked to specific economic activity and the weather system that influences the study area but considered the area as homogeneous. This may not allow planning of timely agricultural input delivery and making provision of adequate training on agricultural extension activities, which are equally a challenge due to rainfall seasonality and variability [35,36]. Thus, there is a need to develop objective-based clustering that is functional for both agricultural and hydrological planning usable at operational scale for maize production. Hence, this study was carried out with the objectives of identifying and mapping homogeneous maize management clusters representing areas with relatively similar physiography, weather pattern, and production scheduling in the southern central Rift Valley of Ethiopia.
2 Materials and methods
2.1 The study area
The study areas are located between Lakes Shala and Abaya in southern part of central Rift Valley of Ethiopia. It encompasses area coverage of 1,021,332 ha residing in over 30 districts located in Oromia region (West Arsi), SNNPR (Halaba, Hadiya, Kembata, Wolayta, and Gedeo) and Sidama region (Figure 1).

Study area and weather stations.
2.2 Data source
A continuous time series of 43 available weather stations located within and in close proximity to the study area were used as source to collect daily rainfall data from January 1991 to December 2020 (Figure 1). Geo-referenced daily minimum and maximum temperatures, rainfall, relative humidity, sunshine hours, and altitude of 30 years were acquired from the National Meteorology and Climate Change Institute (the then National Meteorology Agency), Hawassa Branch Office. Rainfall amount for the months of each growing season and year were summed to form a series of accumulated rainfall data for each season October, November, December, and January (ONDJ), FMAM, and JJAS. Data standardization was applied to the entire database by ranking or counting events based on departures from the local climatology in units of standard deviation using the equation (1) [37]
where X is value, μ reff is mean, and σ reff is standard deviation. Subsequently, L-moments, dispersion, and central tendency were computed for all physiographic and weather variables.
2.3 Independence of samples, homogeneity of variance, and equality of means
Normality test for rainfall across locations and years was carried out by a procedure set by Mishra et al. [38]. Bartlett’s test was applied to rainfall data to verify the homogeneity of variance between the months of the year (12 variances – temporal variability) at each site and among the sites (43 variances – spatial variability) at each of the 12 months of the year following a procedure developed by Steel et al. [39].
2.4 PCA
PCA, a dimensionality reduction tool in multivariate analyses, was used for examining multidimensional data to reveal patterns between objects that would not be apparent in a univariate analysis. The PCA with Varimax rotation was aimed at finding the relative influence of each variable explaining the variance of the system in each separate cluster in ONDJ, FMAM, and JJAS seasons separately [40]. For analysis of the data over the southern central Rift Valley, let A be a(t × i) anomaly matrix of rainfall data over a series of t = 30 years and i = 43 stations. A system of t × i numbers (elements) arranged in a rectangular arrangement along r rows and s columns and bounded by the brackets [] or () was called an r by s matrix as in equation (2).
The elements of the matrix A represented departure of rainfall values from their mean values. PCA was performed to examine the coupling between predictors and predicand. The determinant |A − λI| when expanded would give a polynomial, which is called as characteristic polynomial of matrix A. If,
such that AX = λX, then the vector X was called an eigen vector of A corresponding to the eigen value λ. λ (Lamda) was an eigen value of A and x is its corresponding eigen vector. The covariance or correlation matrix of the dataset was used to derive the coefficients a jj , which are the eigen vectors. Alternatively, x becomes the eigen vector pertaining to the eigen value λ, and vice-versa. If A it is the actual rainfall data at stations i (i = 1, 2…s) in the year t (t = 1, 2…r), the mean value is given in equation (4).
The centered data are given in equation (5) as follow:
The covariance matrix is shown below in equation:
The eigen values {λ j} and the eigen vectors {ϕ ij } of this symmetric matrix were extracted. PCs were a linear combination of the original variables used as predictor variable in multiple linear regressions [40] and composed in general as in equation (7):
This transforms the original time series d jt into the new time series PC jt , orthogonal variables. First few PC jt ’s were generally sufficient to explain the variation in the original data. The eigen vectors {ϕ ij } represented spatial patterns, while (PC) jt could be used to understand temporal variability in the data. Determination of the number of components to be used in PCA was performed using eigen values measuring more than 1 [41,42].
2.5 Cluster analysis
For cluster analysis, a partitioning method was adopted using two algorithms i.e., first hierarchical method was used to divide a set of N data vectors into K non-overlapping clusters (K ≤ N) [43] using identified variables from PCA. Second, each data vector was associated with a centroid by similarity. The Ward’s agglomerative hierarchical algorithm [44,45] was used as dissimilarity measure [46] (equation (8)):
where d ij is the Euclidean distance, n is the number of vectors, X ik is the input image vector and X jk is the comparison image vector. Ward’s algorithm [44] creates groups, minimizing the dissimilarity, or minimizing the total sums of squares within groups, also known as sum of square deviations (SSD). At each stage of the procedure, groups were formed in such a manner that the resultant solution bears the lowest SSD within groups. At these stages, the joints of all possible pairs of groups were considered, and the two resulting smaller SSD were grouped together gathering alike individuals [46].
2.6 Data analysis
The presence of significant difference among clusters was tested using identified variables from PCA with one-way fixed effect ANOVA F test (equation (9)) and comparisons of group means among clusters were carried out by factor analysis provided in SPSS [47].
where SSB is sum of squares between treatments, SSW is the sum of squares within treatments, (k − 1) and (N − k) are the degrees of freedom between and within treatments, respectively [48]. Homogeneity of variance among clusters was tested using Levene test statistic, and robust tests of equality of means were checked for those with homogeneous variance using Welch and Brown–Forsythe statistic [49]. Post hoc comparison of means among clusters was done using Bonferroni method, which is a family contrast comparison method, used to compare with m number of post hoc comparisons to assure m = k(k − 1)/2 possible comparisons where k = the number of groups being considered [50–52]. Finally LSD test was done using equation (10):
where P Bonf is the P value from Bonferroni test, P LSD is the P value from LSD, and m is the group mean of a given cluster.
2.7 Cluster mapping
The clusters were mapped in ArcGIS environment version 10.3 using Inverse Distance Weighting method for better visualization of the results [53]. The clusters assume value of an attribute z at any un-sampled point as a distance-weighted average of sampled points lying within a defined neighborhood. The map of clusters and their altitude, rainfall, soils, texture, and geology was drawn using a 1:125,000 scale.
2.8 Principal component regression
Considering pre-processed or identified variables through PCA as main inputs determining the spatial and temporal variations in the study area, without loss of generality, the regression equation can be given as in equation (11) [54]:
where k is the number of independent variables, ßj ( j = 1, 2, …., k) is the partial regression coefficient, xi is the ith independent variable, y is the dependent variable, and ἐi is the error term corresponding to yi.
3 Results and discussion
3.1 Correlation between predictor variables and distribution of predicand
Strong, positive, and significant association was observed between mean rainfall with latitude (R = 0.556, P < 0.001), STDEV (R = 0.754, P < 0.0001), CV(R = 0.529, P < 0.001), and maximum rainfall (R = 0.937, P < 0.0001) in ONDJ season. However, the association of mean rainfall with mean temperature (R = –0.388, P < 0.05) and minimum temperature (R = –0.432, P < 0.005) was negative and strong in ONDJ period (Table 1). Thus, areas that exhibit higher temperature experience lower mean rainfall in ONDJ period in the study area. Conversely, areas existing in higher latitude experience higher rainfall in ONDJ season. Consequently those variables uncorrelated to mean rainfall in ONDJ period are longitude, altitude, T max, and RFmin. These uncorrelated variables were used in subsequent PCA analysis for ONDJ period. This result is in line with those of Machiwal and his colleagues who elaborated rainfall correlation with geographical factors and statistical parameters [43].
Correlation (R) between the predictor variables before applying PCA
Period | Geographic parameters | Climatic factors | Statistical parameters | |||||||
---|---|---|---|---|---|---|---|---|---|---|
Longitude | Latitude | Altitude | T min | T max | T mean | STDEV | CV | RFmin | RFmax | |
ONDJ | 0.193ns | 0.556** | 0.056ns | –0.432** | –0.229ns | –0.388* | 0.754*** | 0.529** | 0.091ns | 0.937*** |
FMAM | –0.116ns | –0.413* | –0.082ns | 0.048ns | 0.093ns | 0.078ns | 0.603*** | 0.651*** | 0.234ns | 0.876*** |
JJAS | 0.145ns | –0.137ns | –0.088ns | –0.210ns | –0.016ns | –0.134ns | 0.337* | –0.257* | 0.478** | 0.756*** |
Annual | –0.003ns | –0.580** | 0.146ns | –0.352* | –0.146ns | –0.291* | 0.565** | –0.206* | 0.537** | 0.595** |
*, **, *** denotes presence of significant, highly significant, and very highly significant associations, respectively, among variables but ns shows the absence of significant associations.
In FMAM season, the mean rainfall was positively and strongly associated with STDEV (R = 0.603, P < 0.0001), CV (R = 0.651, P < 0.0001), and maximum rainfall (R = 0.876, P < 0.0001); however, the association of mean rainfall was negative with latitude (R = –0.413*, P < 0.05) (Table 1 and Figure 2). The increment in mean rainfall with decrement in latitudes was due to the increased effects of ENSO in low tropical areas, which agrees with reports of Bates et al. [55]. The association of mean annual rainfall was negative with latitude (R = –0.580, P = 0.01), CV (R = –0.206, P = 0.05), T min (R = –0.352, P < 0.05), and T mean (R = –0.291, P < 0.05). Thus, small increment in latitude results in decrement in the mean annual and FMAM rainfall. Conversely, small increment in latitude results in increment of the mean rainfall in ONDJ season. JJAS season marks mainly rainy period for all places in the study area due to which there was no statistical differece in the amount of rain across clusters (Table 1 and Figure 2). Thus, the predictor variables uncorrelated with mean monthly rainfall were T max, altitude, and longitude.

Rainfall distribution in annual, ONDJ, FMAM, and JJAS seasons in the study area.
3.2 Eigen values of different components and their significance level
For ONDJ, three PCs explained 74.7% of magnitude of variance, whereas four variables explained 79.3% of variations for FMAM. For JJAS, three PCs explained 78.2% of variance in annual rainfall, while four variables explained 80.5% of variance (Table 2) using a cutoff point of eigen value 1. This was because the variables with higher eigen values were more important than those with smaller magnitude in explaining the variances and thus contain most of the information of the selected factors. These will be used subsequently as forecasting factors. The 25.3, 20.7, and 21.8% variability unexplained by the model in ONDJ, FMAM, and JJAS seasons meant that there were other factors apart from geographic, climatic, and statistical factors that could be used to elucidate the variation. Thus, the original 12 variables were reduced dimensionally to 3–4 new variables and were used subsequently to explain maximum amount of variance.
Eigen value for ONDJ, FMAM, JJAS, and annual rainfall in the study area
Seasons | Statistic | PC1 | PC2 | PC3 | PC4 | PC5 | PC6 | PC7 | PC8 | PC9 | PC10 | PC11 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
ONDJ | Eigen value | 4.484 | 2.738 | 0.991 | 0.862 | 0.639 | 0.489 | 0.335 | 0.293 | 0.170 | 0.000 | 0.000 |
Proportion | 0.408 | 0.249 | 0.090 | 0.078 | 0.058 | 0.044 | 0.030 | 0.027 | 0.015 | 0.000 | 0.000 | |
Cumulative | 0.408 | 0.656 | 0.747 | 0.825 | 0.883 | 0.927 | 0.958 | 0.985 | 1.000 | 1.000 | 1.000 | |
FMAM | Eigen value | 3.641 | 3.334 | 1.532 | 1.005 | 0.831 | 0.651 | 0.486 | 0.338 | 0.159 | 0.024 | 0.000 |
Proportion | 0.303 | 0.278 | 0.128 | 0.084 | 0.069 | 0.054 | 0.041 | 0.028 | 0.013 | 0.002 | 0.000 | |
Cumulative | 0.303 | 0.581 | 0.709 | 0.793 | 0.862 | 0.916 | 0.957 | 0.985 | 0.998 | 1.000 | 1.000 | |
JJAS | Eigen value | 4.105 | 2.099 | 1.552 | 1.103 | 0.804 | 0.599 | 0.443 | 0.296 | 0.000 | 0.000 | 0.000 |
Proportion | 0.373 | 0.191 | 0.141 | 0.100 | 0.073 | 0.054 | 0.040 | 0.027 | 0.000 | 0.000 | 0.000 | |
Cumulative | 0.373 | 0.564 | 0.705 | 0.805 | 0.878 | 0.933 | 0.973 | 1.000 | 1.000 | 1.000 | 1.000 | |
Annual | Eigen value | 4.486 | 2.787 | 1.334 | 0.860 | 0.529 | 0.495 | 0.240 | 0.171 | 0.094 | 0.004 | 0.000 |
Proportion | 0.408 | 0.253 | 0.121 | 0.078 | 0.048 | 0.045 | 0.022 | 0.016 | 0.009 | 0.000 | 0.000 | |
Cumulative | 0.408 | 0.661 | 0.782 | 0.861 | 0.909 | 0.954 | 0.976 | 0.991 | 1.000 | 1.000 | 1.000 |
The maximum degree of variability in the dataset was expressed with the first four components in FMAM period. Thus, PC1, PC2, PC3, and PC4 explained 30.3, 27.8, 12.8, and 8.4% of variance, respectively (Table 2). FMAM is important because land preparation, planting, urea application, and weeding are carried for maize crop in the majority of the study areas. In all the seasons, PC1 was mean rainfall component with strong association with altitude and longitude, but strong negative association with T min, T max, and T mean (Table 3) implying the dynamics of the ITCZ over the study area [56,57]. This was in turn due to a high elevation leading to low temperatures (an increase in 1,000 m in altitude leads to a decrease of 6.5°C in temperature). This result is in agreement with reports of Belay in the Beles basin of Ethiopia, who reported inverse relationship among mean temperatures and elevations [58]. PC2 was termed as temperature component and showed strong positive association with latitude but strong to moderate negative association with altitude. The variables that correlate most with PC1 are RFmean (0.401), RFmax (0.478), and variance (0.400). The first PC is positively correlated with these three variables. Therefore, increasing the value of RFmean, RFmax, and variance subsequently increases the value of PC1 (Table 3). The variables positively associated with PC2 were T min (0.456), T max (0.433), and T mean (0.511). This summarizes the direction of eigen vectors.
Eigen vectors for FMAM rainfall
Variable | PC1 | PC2 | PC3 | PC4 | PC5 | PC6 | PC7 | PC8 | PC9 | PC10 | PC11 |
---|---|---|---|---|---|---|---|---|---|---|---|
Latitude | –0.330 | 0.105 | –0.041 | –0.269 | –0.388 | 0.725 | 0.109 | –0.028 | 0.343 | 0.003 | 0.000 |
Longitude | –0.199 | –0.254 | 0.006 | –0.410 | 0.598 | –0.034 | 0.586 | –0.104 | 0.118 | 0.021 | 0.000 |
T min | 0.075 | 0.456 | 0.191 | 0.011 | –0.153 | –0.165 | 0.459 | 0.518 | 0.037 | –0.005 | 0.256 |
T max | 0.194 | 0.433 | –0.165 | –0.095 | 0.140 | 0.194 | 0.018 | –0.616 | –0.349 | 0.041 | 0.231 |
T mean | 0.151 | 0.511 | 0.025 | –0.045 | –0.016 | 0.006 | 0.287 | –0.023 | –0.168 | 0.019 | –0.424 |
Altitude | –0.205 | –0.374 | 0.281 | 0.148 | –0.342 | 0.112 | 0.345 | –0.069 | –0.674 | 0.096 | 0.000 |
RFmean | 0.401 | –0.086 | 0.426 | –0.237 | 0.104 | 0.222 | –0.149 | 0.103 | –0.020 | 0.217 | –0.564 |
RFmin | –0.137 | 0.143 | 0.715 | –0.091 | 0.198 | 0.080 | –0.242 | –0.071 | –0.031 | –0.470 | 0.279 |
Rfmax | 0.478 | –0.160 | 0.074 | –0.196 | 0.006 | 0.187 | –0.030 | 0.142 | –0.005 | 0.459 | 0.553 |
Var | 0.400 | –0.198 | –0.339 | –0.133 | 0.020 | 0.265 | 0.076 | 0.276 | –0.234 | –0.679 | –0.000 |
STDEV | 0.242 | –0.082 | 0.133 | 0.752 | 0.205 | 0.325 | 0.296 | –0.149 | 0.302 | –0.047 | –0.000 |
CV | –0.341 | 0.172 | –0.159 | 0.200 | 0.489 | 0.360 | –0.238 | 0.449 | –0.339 | 0.216 | 0.000 |
3.3 Rotated factor loadings and communalities
After Varimax rotation, the PC results showed that T mean (0.960), T max (0.895), and T min (0.784) had large positive loadings on factor 1 (Table 4). Hence, their increment is vital for homogenous clustering. Whereas altitude (–0.829) has large negative loading on factor 1 and thus acted as a base for heterogeneity. RFmean (0.927) and RFmax (0.942) have large positive loadings on factor 2 (Table 4; Figures 3–6). Bilate, Bulbula, Aje, Alaba Kulito, Humbo, and Ropi had high loadings with PC2, whereas Dilla, Humbo, Seraro, and Shone locations had high loadings with PC1 (Figure 3). The lowest loadings with PC1 were Woteraresa and wondo genet whereas the lowest loadings with PC2 were Woteraresa, Tefer Kela, and Yirgalem (Figure 3). The mean rainfall in FMAM was also meager in places like Aje, Ropi, Seraro, and Abaya. Conversely Wolaita Sodo, Yirgalem, Tefer Kela, Hawassa, Wondoget, Abaro, Boditi, Shamana, Durame, and Maykote received quit good rain in FMAM season (Figure 3).
Sorted rotated factor loadings and communalities for FMAM season
Variable | Factor 1 | Factor 2 | Factor 3 | Factor 4 | Communality |
---|---|---|---|---|---|
Latitude | –0.017 | –0.496 | 0.174 | –0.481 | 0.508 |
Longitude | –0.529 | –0.022 | 0.006 | –0.499 | 0.529 |
T min | 0.784 | –0.065 | 0.383 | 0.066 | 0.769 |
T mean | 0.960 | –0.019 | 0.179 | 0.034 | 0.955 |
T max | 0.895 | 0.038 | –0.096 | –0.010 | 0.811 |
Altitude | –0.829 | –0.063 | 0.259 | 0.068 | 0.762 |
RFmean | 0.072 | 0.927 | 0.254 | 0.120 | 0.943 |
RFmin | 0.032 | 0.009 | 0.960 | –0.066 | 0.928 |
RFmax | 0.057 | 0.942 | –0.225 | 0.156 | 0.965 |
STDEV | –0.059 | 0.204 | –0.025 | 0.887 | 0.832 |
CV | 0.069 | –0.766 | 0.063 | –0.076 | 0.602 |
% Var | 0.277 | 0.256 | 0.149 | 0.111 | 0.793 |

Score plot of observations for PC1 and PC2.

Bi-plot of variables used in PCA analysis.

Agglomeration schedule coefficients.

Dendrogram using ward linkage.
When the contribution of each variable to the linear combinations was considered, longitude and altitude had strong negative influence on PC2 (Figure 4). But T mean had strong positive influence on PC2. Similarly, RFmin exerted weak influence on PC1 (Figure 4).
3.4 Cluster analysis
The agglomeration schedule coefficients end at 42 (right top) whereas the elbow of the graph breaks sharply at 38 (left). The difference between the top unit and elbow is four clusters (Figure 5). This result of agglomeration schedule coefficients was verified by employing dendrogram method that automatically generated four relatively homogeneous units in the study area (Figure 6). Locations in one cluster are more similar to one another than locations in another cluster within a given season with climatic, environmental, geological, and physiographic features. Thus, four clusters were formed namely cluster I (Shamana cluster), cluster II (Bilate cluster), cluster III (Hawassa cluster), and cluster IV (Dilla cluster) (Figures 5–7).

The location of the four clusters.
3.5 Map and attributes of clusters
Cluster II locations had largest area (388,193 ha) whereas cluster IV areas had smallest area (121,931 ha). The area coverage of clusters I (324,242 ha) and III (186,966 ha) were intermediate (Figure 7). The records of annual and JJAS rainfall were highest in cluster IV. The wettest cluster during ONDJ is also cluster IV with mean rainfall of 299.2 + 51.3 mm across the 4 months of ONDJ (Table 5). Cluster I areas include high altitude maize growing areas in Abaro, Duguna Fango, Damot Gale, Badawacho, Shala, Seraro, Haisawita, Shashamane, Telamokantise, Aleta Wendo, Woteraresa, and Wujegra. In these areas, tillage operation begins early in November and planting maize starts with some rainfall showers from mid-December to mid-January unlike the other clusters. The areas in cluster II include low-altitude areas in Humbo, Halaba, Seraro, Bedessa, Bilate Tena, Bilate, Alaba Kulito, Shala, and Bulbula. These areas obtained 758.7 ± 125.8 mm of rain on average every year. ONDJ period was critically dry in clusters II and III and hence, was unable to support agricultural operations including tillage practices. In the next FMAM season, all clusters receive fairly good rain, except cluster II (Table 5). Hence, planting maize is usually delayed up to the beginning of May in cluster II areas. The 3rd cluster also called Hawassa cluster includes mid-altitude areas of Badawacho, Hawassa, Seraro, Shashamane, Boricha, Balela, Halaba, Humbo, Wolaita Sodo, and Bedessa. The areas included in cluster IV were lowland to mid-altitude areas in Aleta Wendo, Dilla, Tefer Kela, Dara, and Chuko. Maize is usually grown as of March within the agro-forestry system in this area. Thus, a given administrative district had more than one clusters, and careful arrangements are required even within a district in planning extension service, input delivery, and agromet advisories. This finding is in agreement with elucidation of Befikadu et al. [59] who partitioned adjacent districts into Bilate lowlands, Wolaita Sodo midlands, and Boditi highland. The Bilate cluster represented maize production agro-ecology termed as semiarid lowlands of central Rift Valley or dry mid-altitudes by Abate et al. [1] and low moisture areas by Worku et al. [60]. The Hawassa cluster was one of the sub-moist mid altitude areas in central Rift Valley in which is also called mid-altitude sub-humid by Worku et al. [60]. The Shamana cluster stands for highland transitional moist areas with upper mid-altitudes category as reported by Abate et al. [1] or highland sub-humid areas as stated by Worku et al. [60]. Finally low to mid altitude areas adjacent to mountain chains of Sidama and Gedeo were grouped into Dilla cluster and represented as humid tropics by Shengu [61], moist lower mid-altitudes by Abate et al. [1], and as lowland sub-humid areas by Worku et al. [60].
Descriptive statistics of cluster-wise mean rainfall for different seasons
Clusters | ONDJ | FMAM | JJAS | Annual | ||||
---|---|---|---|---|---|---|---|---|
Station | RFmean | Station | RFmean | Station | RFmean | Station | RFmean | |
Cluster I | 2 | 290.9 ± 30.2 | 9 | 274.8 ± 121 | 4 | 406.3 ± 143.1 | 2 | 972.0 ± 97.8 |
Cluster II | 9 | 212.7 ± 45.2 | 14 | 224.6 ± 79.6 | 4 | 321.4 ± 47.1 | 11 | 758.7 ± 125.8 |
Cluster III | 25 | 260.6 ± 44.6 | 16 | 277.5 ± 24.6 | 25 | 415.8 ± 17.8 | 22 | 953.9 ± 57.5 |
Cluster IV | 7 | 299.2 ± 51.3 | 4 | 399.8 ± 62.6 | 10 | 599.2 ± 33.8 | 8 | 1,298.2 ± 70.4 |
The presence of diverse maize production and recommendation domains were also reported by Alemu et al. [62] who elaborated high altitude sub-humid, low altitude sub-humid, mid altitude sub-humid, and moisture stressed places in the country. Thus, the highland, mid-altitude, and lowland areas are grouped into four clusters having different agro-ecology, cropping season, and choice of varieties, and consequently require different input delivery and training arrangement.
3.6 Geology, parent materials, and soils
In Shamana cluster, soils are developed from volcanic sedimentary to lacustrine deposits and have relatively higher clay and dominantly belong to Vertic Luvisols, Eutric Cambisols, and Chromic Vertisols based on FAO soil classification [63] (Figure 8). However, in Bilate cluster, the most dominant soil is riverine or lacustrine alluvium derived from basalt, ignimbrite, lava, or ash with dark brown loamy coarse sands and sandy loams with often calcareous subsoil, and belong to Calcaric Fluvisol, Orthic Andosol, Ortic Phaeozems, and Chromic Luivisols. In Hawassa cluster, the dominant soils are Vitric Andosols, Eutric Cambisols, and Leptosols. The soils had lacustrine and pyroclastic deposits of sands and silts, interbedded with pumice (Figure 8). In Dilla cluster the soils are originated from basalt rocks, and had deep reddish to brown clayey to clay loam texture classified as Haplic Luvisols and Chromic Vertisols (Figure 8).

Geology, altitude, and textural class of soils in the four clusters.
Low bulk density and weak structure of soils in Bilate and Hawassa clusters render them vulnerable to erosion even on gentle slopes compared to those in Shamana and Dilla clusters. The altitude of the study area ranges from 1,174 m a.s.l. at Lake Abaya (Cluster II) to 3,160 m a.s.l. at Woteraresa (Cluster I) (Figure 8), which leads to dramatic variability in environmental conditions among clusters over relatively short distances.
3.7 Evaluation statistics among clusters for FMAM season
Each cluster was distinct and heterogeneous in climatic, physical, and statistical variables (Table 6). There were four clusters in FMAM season as dictated by altitude, RFmin, and T min with 9, 14, 16, and 4 cluster members in clusters I, II, III, and IV, respectively. Cluster II had highest T min (22.7°C), lowest RFmin (86.1 mm), and lowest altitude (1,701 m a.s.l.). Cluster I areas have lowest T min (22.7°C) but highest altitude (2,180 m a.s.l.) (Table 6).
Descriptive statistics for the most significant variables in FMAM season
PC | Clusters | N | Mean | Std. deviation | Std. error | 95% CI for mean | Mini mum | Maxi mum | |
---|---|---|---|---|---|---|---|---|---|
Lower bound | Upper bound | ||||||||
T min | Cluster I | 9 | 18.9 | 1.19 | 0.38 | 18.09 | 19.79 | 16.50 | 20.40 |
(°C) | Cluster II | 14 | 22.7 | 0.83 | 0.24 | 22.17 | 23.23 | 21.90 | 24.40 |
Cluster III | 16 | 21.0 | 0.51 | 0.12 | 20.73 | 21.24 | 20.00 | 22.10 | |
Cluster IV | 4 | 19.2 | 0.72 | 0.42 | 17.41 | 20.99 | 18.40 | 19.80 | |
Total | 43 | 20.9 | 1.63 | 0.25 | 20.36 | 21.37 | 16.50 | 24.40 | |
RFmin | Cluster I | 9 | 87.5 | 47.0 | 14.9 | 53.9 | 121.1 | 2.7 | 148.9 |
(mm) | Cluster II | 14 | 86.1 | 61.1 | 17.6 | 47.3 | 125.0 | 8.4 | 220.6 |
Cluster III | 16 | 107.3 | 86.4 | 20.4 | 64.4 | 150.3 | 11.5 | 313.1 | |
Cluster IV | 4 | 352.8 | 80.1 | 46.2 | 153.9 | 551.7 | 262.7 | 415.7 | |
Total | 43 | 113.9 | 96.2 | 14.7 | 84.3 | 143.5 | 2.7 | 415.7 | |
Altitude | Cluster I | 9 | 2,180 | 251 | 79 | 2,001 | 2,360 | 1,876 | 2,631 |
(m a.s.l.) | Cluster II | 14 | 1,701 | 247 | 71 | 1,544 | 1,858 | 1,182 | 2,023 |
Cluster III | 16 | 1,804 | 147 | 35 | 1,731 | 1,877 | 1,515 | 2,116 | |
Cluster IV | 4 | 1,785 | 86 | 50 | 1,571 | 1,998 | 1,698 | 1,870 | |
Total | 43 | 1,861 | 268 | 41 | 1,779 | 1,944 | 1,182 | 2,631 |
The ANOVA table showed that F-test was significantly (P < 0.001) different among clusters for T min, RFmin, and Altitude (Table 7).
ANOVA table for uncorrelated variables of rainfall in FMAM season
Variables | Source of variation | Sum of squares | df | Mean square | F | Sig. |
---|---|---|---|---|---|---|
T min | Between groups | 86.0559 | 3 | 28.6853 | 43.3249 | 1.72 × 10−12 |
Within groups | 25.82178 | 39 | 0.662097 | |||
Total | 111.8777 | 42 | ||||
RFmin | Between groups | 188270.3 | 3 | 62756.76 | 12.1962 | 9.01 × 10−6 |
Within groups | 200677.3 | 39 | 5145.571 | |||
Total | 388947.6 | 42 | ||||
Altitude | Between groups | 1,400,502 | 3 | 466833.9 | 11.2207 | 1.91 × 10−5 |
Within groups | 1,622,581 | 39 | 41604.64 | |||
Total | 3,023,083 | 42 |
The mean separation based on Bonferroni technique showed that cluster I had significantly lower temperature by value of 3.76 and 2.05°C compared to clusters II and III, respectively. The difference in mean temperature between cluster I and cluster IV was not significantly different (P < 0.05). The significantly lower temperature in cluster I areas like Abaro, Bitena, Boditi, Haisawita, Mayokote, Shamana, Shone, Telamokantise, Woteraresa, and Wujegra could be due to higher rainfall received in the previous months that actually have cooling effect in the area. Cluster II areas with significantly higher T mean compared to other clusters were Abaya, Alaba Kulito, Bilate, Bilate Tena, Bulbula, Chuko, Dilla, Felka, Hawassa, Humbo, Morocho, and Seraro. These were the areas extending from Lake Shala to Lake Abaya and lie in the central part of Rift Valley. The difference in minimum rainfall received in FMAM was significantly higher in cluster IV by 265, 267, and 246 mm in clusters I, II, and III, respectively. Similarly, significantly higher means of altitudes were measured in clusters I than cluster II (P < 0.001), III (P < 0.001), and IV (P < 0.05) by value of 479, 376, and 395 m, respectively (Table 8).
Multiple comparisons and post hoc tests of PCs in FMAM season
PCs | Mean difference (I − J) | Std. error | Sig. | 95% Confidence interval | |||
---|---|---|---|---|---|---|---|
Pairwise comparison | Lower bound | Upper bound | |||||
T mean | Cluster I | Cluster II | –3.76 | 0.35 | 0.00 | –4.73 | –2.79 |
(°C) | Cluster III | –2.05 | 0.32 | 0.00 | –2.94 | –1.16 | |
Cluster IV | –0.26 | 0.54 | 1.00 | –1.75 | 1.23 | ||
Cluster II | Cluster I | 3.76 | 0.35 | 0.00 | 2.79 | 4.73 | |
Cluster III | 1.71 | 0.30 | 0.00 | 0.87 | 2.55 | ||
Cluster IV | 3.50 | 0.53 | 0.00 | 2.04 | 4.96 | ||
Cluster III | Cluster I | 2.05 | 0.32 | 0.00 | 1.16 | 2.94 | |
Cluster II | –1.71 | 0.30 | 0.00 | –2.55 | –0.87 | ||
Cluster IV | 1.79 | 0.51 | 0.01 | 0.38 | 3.20 | ||
Cluster IV | Cluster I | 0.26 | 0.54 | 1.00 | –1.23 | 1.75 | |
Cluster II | –3.50 | 0.53 | 0.00 | –4.96 | –2.04 | ||
Cluster III | –1.79 | 0.51 | 0.01 | –3.20 | –0.38 | ||
RFmin | Cluster I | Cluster II | 1.36 | 30.71 | 1.00 | –84.02 | 86.73 |
(mm) | Cluster III | –19.84 | 28.29 | 1.00 | –98.48 | 58.80 | |
Cluster IV | –265.34 | 47.22 | 0.00 | –396.60 | –134.09 | ||
Cluster II | Cluster I | –1.36 | 30.71 | 1.00 | –86.73 | 84.02 | |
Cluster III | –21.20 | 26.73 | 1.00 | –95.51 | 53.11 | ||
Cluster IV | –266.70 | 46.30 | 0.00 | –395.40 | –138.00 | ||
Cluster III | Cluster I | 19.84 | 28.29 | 1.00 | –58.80 | 98.48 | |
Cluster II | 21.20 | 26.73 | 1.00 | –53.11 | 95.51 | ||
Cluster IV | –245.50 | 44.73 | 0.00 | –369.84 | –121.16 | ||
Cluster IV | Cluster I | 265.34 | 47.22 | 0.00 | 134.09 | 396.60 | |
Cluster II | 266.70 | 46.30 | 0.00 | 138.00 | 395.40 | ||
Cluster III | 245.50 | 44.73 | 0.00 | 121.16 | 369.84 | ||
Altitude | Cluster I | Cluster II | 478.82 | 87.34 | 0.00 | 236.07 | 721.58 |
(m) | Cluster III | 376.20 | 80.45 | 0.00 | 152.59 | 599.81 | |
Cluster IV | 395.36 | 134.27 | 0.03 | 22.15 | 768.58 | ||
Cluster II | Cluster I | –478.82 | 87.34 | 0.00 | –721.58 | –236.07 | |
Cluster III | –102.63 | 76.02 | 1.00 | –313.92 | 108.67 | ||
Cluster IV | –83.46 | 131.66 | 1.00 | –449.43 | 282.51 | ||
Cluster III | Cluster I | –376.20 | 80.45 | 0.00 | –599.81 | –152.59 | |
Cluster II | 102.63 | 76.02 | 1.00 | –108.67 | 313.92 | ||
Cluster IV | 19.17 | 127.20 | 1.00 | –334.39 | 372.72 | ||
Cluster IV | Cluster I | –395.36 | 134.27 | 0.03 | –768.58 | –22.15 | |
Cluster II | 83.46 | 131.66 | 1.00 | –282.51 | 449.43 | ||
Cluster III | –19.17 | 127.20 | 1.00 | –372.72 | 334.39 |
3.8 Seasonal rainfall prediction
As maize is planted in FMAM season and continues to grow in JJAS period, the two seasons are important for rain-fed maize production. Additionally, sea surface temperature and T mean are not included in regression equation mainly because the former shows little variation across clusters [11] and the latter has well-established inverse relationship with altitude in Ethiopia [7,58], which necessitates reduction in input variables and associated redundancies. Hence, the percentage of the variance in mean rainfall is explained by local factors including altitude, latitude, and longitude. As depicted by regression of geographical and topographic parameters (predictors) on rainfall (predicand), coefficient of determination (R²) is greater than 0.50 for most of the seasons and clusters (Table 9). Latitude (ß1) and longitude (ß2) showed negative regression coefficients for most of the clusters across the seasons unlike altitude (ß3) which showed positive regression coefficients. Hence, latitude showed significant and negative prediction on mean rainfall in third cluster in ONDJ and annual seasons, and also first cluster in annual season. Thus, areas in southern part of the study site (for instance, Dilla) would receive more rainfall compared to northern areas (for instance, Shala) (Figure 8). In FMAM season, cluster I areas lying in lower longitude and cluster IV areas located in lower altitude are going to receive higher rainfall (Table 9). Similarly, cluster II areas lying in relatively higher altitude are going to receive higher rainfall in JJAS season. Thus, there is a need to prioritize mitigation measures in cluster II areas lying in lower altitude and cluster I areas situated in higher longitude in the future. This agrees with findings of Teodoro et al. [64] who showed altitude followed by latitude as an important physiographic factor that influence the monthly rainfall behavior in dry, transitional, and rainy periods.
Estimate of the parameters (ß1, ß2, ß3 and R 2) of the multiple linear regression and coefficient of determination (R²) of average seasonal rainfall according to altitude (m), latitude (decimal degrees), and longitude (decimal degrees), in southern central Ethiopia
Season | Cluster | Constant | Latitude (ß1) | Longitude (ß2) | Altitude (ß3) | R 2 |
---|---|---|---|---|---|---|
ONDJ | Cluster I | 759 | –90.9ns | –1.7ns | 0.0835* | 0.746 |
Cluster II | 314 | –9.3ns | –5.3ns | 0.0798** | 0.889 | |
Cluster III | 147 | –370* | 4.2ns | 0.0832** | 0.513 | |
Cluster IV | 5,702 | 22.7ns | –153ns | 0.1251* | 0.910 | |
FMAM | Cluster I | 1,821 | –37.8ns | –37.9* | –0.0237ns | 0.707 |
Cluster II | 1,342 | –47.4ns | –27.2ns | 0.0552ns | 0.461 | |
Cluster III | –654 | –31ns | –31ns | 0.0105ns | 0.532 | |
Cluster IV | 23,753 | –81.7ns | –81.7ns | –0.2240** | 0.969 | |
JJAS | Cluster I | –815 | 3ns | 27.2ns | –0.0642ns | 0.619 |
Cluster II | 2,246 | 27.1ns | –67.7ns | 0.0981* | 0.689 | |
Cluster III | 126 | –23.1ns | 4.1ns | –0.002ns | 0.515 | |
Cluster IV | 12,092 | 135ns | –335ns | 0.0004ns | 0.487 | |
Annual | Cluster I | 23,467 | –2,481* | –128ns | 0.045ns | 0.863 |
Cluster II | 23,524 | –69ns | –601ns | 0.597ns | 0.564 | |
Cluster III | 21,227 | –5,791* | –404* | –0.223ns | 0.632 | |
Cluster IV | –205,370 | –1,510ns | 566.7ns | –0.283ns | 0.713 |
ns, *, and ** are not significant, significant at 5 and 1% probability, respectively, by t-test, with 42° of freedom.
4 Conclusion
This study examined the PCs responsible for agro-ecological variations and the spatial patterns of ONDJ, FMAM, JJAS, and annual rainfall in the dominant maize producing areas of south central Rift Valley of Ethiopia. Using 12 geographical, statistical, and agro-climatic variables for a period of 30 years from 43 weather stations within or nearby the study area and by applying integrating methods like PCA, spatial clustering, and interpolation, we were able to quantify and delineate the distinct clusters that require specific agronomic decisions by farmers, researchers, and policy makers. The PCA resulted in three to four significant PCs explaining 74.7% of variance for ONDJ, 79.3% of variations in FMAM, 80.5% of variance in JJAS, and 78.2% of variance in annual rainfall. The hierarchical cluster analysis that integrated the identified PC’s resulted in four statistically distinct clusters.
Latitude had strong influence on rainfall component (PC1). Longitude and altitude had strong influence on temperature component (PC2). Mean rainfall influenced PC3 strongly. Thus, the original ecological factors which determined the formation of clusters in the study area were T mean, latitude, longitude, altitude, and RFmean. The Shamana cluster has soils with high clay content and characterized by high altitude, low temperature, and higher rainfall components in ONDJ season. The Bilate cluster has course sand to sandy loam soils, and characterized by low altitude and high temperature components across most seasons. The Hawassa cluster possesses soils with dominant sand and silt mixtures, and has intermediate altitude, temperature, and rainfall components in most seasons. The Dilla cluster has clayey to clay loam soils and characterized by high rainfall components in JJAS and annual seasons. The results also showed that rainfall decreased and rainfall variability increased at higher longitudes and lower altitudes showing significant future risks in clusters I, II, and IV areas. Hence, any planning and management activity related to maize production should recognize the ecological distinctness of the clusters from one another. The findings of this study depicted that areas differing in biophysical potential should be treated independently during inputs delivery, agricultural planning, and designing of adaptation strategies to maximize productivity and reduce risks associated with agricultural production. Hence, the national and regional governments should establish different sets of input delivery, extension, and agromet advisory programs for each cluster and the local government should play a proactive role to manage cluster-wise schedules. Moreover, future research work shall embody rainfall characteristics and its variability in each of these clusters and develop operational maize calendar usable at grass root level.
Acknowledgments
The authors acknowledge Hawassa University College of Agriculture School of Plant and Horticultural Sciences for allowing to join the PhD program in Agronomy and the National Meteorology and Climate Change Institute (the then National Meteorology Agency), Hawassa Branch Office for provision of geo-referenced weather data, and Southern Agriculture Research Institute (SARI) for provision of required funds to procure weather data.
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Funding information: The authors obtained data procurement fund from Southern Agriculture Research Institute (SARI).
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Author contributions: D.M. and G.M. – conceptualization, formal analysis, methodology, and writing – original draft; D.M. – Data collection and resources; and W.W. – writing – review and editing.
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Conflict of interest: The authors state no conflict of interest.
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Data availability statement: The datasets generated during and/or analyzed during the current study are available from the corresponding author on reasonable request.
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This work is licensed under the Creative Commons Attribution 4.0 International License.
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- Regular Articles
- Foliar application of boron positively affects the growth, yield, and oil content of sesame (Sesamum indicum L.)
- Impacts of adopting specialized agricultural programs relying on “good practice” – Empirical evidence from fruit growers in Vietnam
- Evaluation of 11 potential trap crops for root-knot nematode (RKN) control under glasshouse conditions
- Technical efficiency of resource-poor maize farmers in northern Ghana
- Bulk density: An index for measuring critical soil compaction levels for groundnut cultivation
- Efficiency of the European Union farm types: Scenarios with and without the 2013 CAP measures
- Participatory validation and optimization of the Triple S method for sweetpotato planting material conservation in southern Ethiopia
- Selection of high-yield maize hybrid under different cropping systems based on stability and adaptability parameters
- Soil test-based phosphorus fertilizer recommendation for malting barley production on Nitisols
- Effects of domestication and temperature on the growth and survival of the giant freshwater prawn (Macrobrachium rosenbergii) postlarvae
- Influence of irrigation regime on gas exchange, growth, and oil quality of field grown, Texas (USA) olive trees
- Present status and prospects of value addition industry for agricultural produce – A review
- Competitiveness and impact of government policy on chili in Indonesia
- Growth of Rucola on Mars soil simulant under the influence of pig slurry and earthworms
- Effect of potassium fertilizer application in teff yield and nutrient uptake on Vertisols in the central highlands of Ethiopia
- Dissection of social interaction and community engagement of smallholder oil palm in reducing conflict using soft system methodology
- Farmers’ perception, awareness, and constraints of organic rice farming in Indonesia
- Improving the capacity of local food network through local food hubs’ development
- Quality evaluation of gluten-free biscuits prepared with algarrobo flour as a partial sugar replacer
- Effect of pre-slaughter weight on morphological composition of pig carcasses
- Study of the impact of increasing the highest retail price of subsidized fertilizer on rice production in Indonesia
- Agrobiodiversity and perceived climatic change effect on family farming systems in semiarid tropics of Kenya
- Influences of inter- and intra-row spacing on the growth and head yield of cabbage (Brassica oleracea var. capitata) in western Amhara, Ethiopia
- The supply chain and its development concept of fresh mulberry fruit in Thailand: Observations in Nan Province, the largest production area
- Toward achieving sustainable development agenda: Nexus between agriculture, trade openness, and oil rents in Nigeria
- Phenotyping cowpea accessions at the seedling stage for drought tolerance in controlled environments
- Apparent nutrient utilization and metabolic growth rate of Nile tilapia, Oreochromis niloticus, cultured in recirculating aquaculture and biofloc systems
- Influence of season and rangeland-type on serum biochemistry of indigenous Zulu sheep
- Meta-analysis of responses of broiler chickens to Bacillus supplementation: Intestinal histomorphometry and blood immunoglobulin
- Weed composition and maize yield in a former tin-mining area: A case study in Malim Nawar, Malaysia
- Strategies for overcoming farmers’ lives in volcano-prone areas: A case study in Mount Semeru, Indonesia
- Principal component and cluster analyses based characterization of maize fields in southern central Rift Valley of Ethiopia
- Profitability and financial performance of European Union farms: An analysis at both regional and national levels
- Analysis of trends and variability of climatic parameters in Teff growing belts of Ethiopia
- Farmers’ food security in the volcanic area: A case in Mount Merapi, Indonesia
- Strategy to improve the sustainability of “porang” (Amorphophallus muelleri Blume) farming in support of the triple export movement policy in Indonesia
- Agrarian contracts, relations between agents, and perception on energy crops in the sugarcane supply chain: The Peruvian case
- Factors influencing the adoption of conservation agriculture by smallholder farmers in KwaZulu-Natal, South Africa
- Meta-analysis of zinc feed additive on enhancement of semen quality, fertility and hatchability performance in breeder chickens
- Meta-analysis of the potential of dietary Bacillus spp. in improving growth performance traits in broiler chickens
- Biocomposites from agricultural wastes and mycelia of a local mushroom, Lentinus squarrosulus (Mont.) Singer
- Cross transferability of barley nuclear SSRs to pearl millet genome provides new molecular tools for genetic analyses and marker assisted selection
- Detection of encapsulant addition in butterfly-pea (Clitoria ternatea L.) extract powder using visible–near-infrared spectroscopy and chemometrics analysis
- The willingness of farmers to preserve sustainable food agricultural land in Yogyakarta, Indonesia
- Transparent conductive far-infrared radiative film based on polyvinyl alcohol with carbon fiber apply in agriculture greenhouse
- Grain yield stability of black soybean lines across three agroecosystems in West Java, Indonesia
- Forms of land access in the sugarcane agroindustry: A comparison of Brazilian and Peruvian cases
- Assessment of the factors contributing to the lack of agricultural mechanization in Jiroft, Iran
- Do poor farmers have entrepreneurship skill, intention, and competence? Lessons from transmigration program in rural Gorontalo Province, Indonesia
- Communication networks used by smallholder livestock farmers during disease outbreaks: Case study in the Free State, South Africa
- Sustainability of Arabica coffee business in West Java, Indonesia: A multidimensional scaling approach
- Farmers’ perspectives on the adoption of smart farming technology to support food farming in Aceh Province, Indonesia
- Rice yield grown in different fertilizer combination and planting methods: Case study in Buru Island, Indonesia
- Paclobutrazol and benzylaminopurine improve potato yield grown under high temperatures in lowland and medium land
- Agricultural sciences publication activity in Russia and the impact of the national project “Science.” A bibliometric analysis
- Storage conditions and postharvest practices lead to aflatoxin contamination in maize in two counties (Makueni and Baringo) in Kenya
- Relationship of potato yield and factors of influence on the background of herbological protection
- Biology and life cycle Of Diatraea busckella (Lepidoptera: Crambidae) under simulated altitudinal profile in controlled conditions
- Evaluation of combustion characteristics performances and emissions of a diesel engine using diesel and biodiesel fuel blends containing graphene oxide nanoparticles
- Effect of various varieties and dosage of potassium fertilizer on growth, yield, and quality of red chili (Capsicum annuum L.)
- Review Articles
- Germination ecology of three Asteraceae annuals Arctotis hirsuta, Oncosiphon suffruticosum, and Cotula duckittiae in the winter-rainfall region of South Africa: A review
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- Short Communication
- Response of cannabidiol hemp (Cannabis sativa L.) varieties grown in the southeastern United States to nitrogen fertilization
- Special Issue on the International Conference on Multidisciplinary Research – Agrarian Sciences
- Special issue on the International Conference on Multidisciplinary Research – Agrarian Sciences: Message from the editor
- Maritime pine land use environmental impact evolution in the context of life cycle assessment
- Influence of different parameters on the characteristics of hazelnut (var. Grada de Viseu) grown in Portugal
- Organic food consumption and eating habit in Morocco, Algeria, and Tunisia during the COVID-19 pandemic lockdown
- Customer knowledge and behavior on the use of food refrigerated display cabinets: A Portuguese case
- Perceptions and knowledge regarding quality and safety of plastic materials used for food packaging
- Understanding the role of media and food labels to disseminate food related information in Lebanon
- Liquefaction and chemical composition of walnut shells
- Validation of an analytical methodology to determine humic substances using low-volume toxic reagents
- Special Issue on the International Conference on Agribusiness and Rural Development – IConARD 2020
- Behavioral response of breeder toward development program of Ongole crossbred cattle in Yogyakarta Special Region, Indonesia
- Special Issue on the 2nd ICSARD 2020
- Perceived attributes driving the adoption of system of rice intensification: The Indonesian farmers’ view
- Value-added analysis of Lactobacillus acidophilus cell encapsulation using Eucheuma cottonii by freeze-drying and spray-drying
- Investigating the elicited emotion of single-origin chocolate towards sustainable chocolate production in Indonesia
- Temperature and duration of vernalization effect on the vegetative growth of garlic (Allium sativum L.) clones in Indonesia
- Special Issue on Agriculture, Climate Change, Information Technology, Food and Animal (ACIFAS 2020)
- Prediction model for agro-tourism development using adaptive neuro-fuzzy inference system method
- Special Issue of International Web Conference on Food Choice and Eating Motivation
- Can ingredients and information interventions affect the hedonic level and (emo-sensory) perceptions of the milk chocolate and cocoa drink’s consumers?