1. Introduction
Drought is a recurrent climatic phenomenon all over the world, which varies every time it occurs in terms of its magnitude, severity, duration, and geographical coverage. Drought episodes have been recurring for many years in Africa and have affected humanity in many ways, such as causing loss of life, crop failures, and food shortages. These, in turn, have triggered famine in many regions, resulting in malnutrition, health issues, and mass migration [
1,
2,
3].
Previous research found that more than 10 million people died due to drought impacts from 1900–2010 in the world [
3,
4]. In 2003 and 2006, Europe was hit by severe droughts that caused crop failures, navigation problems, and loss of life due to a heat wave [
5]. In addition, until 2008, the Iberian Peninsula faced impacts of the latter drought that extended for multiple years, reducing groundwater levels and reservoir storage to a minimum [
6]. In Africa, drought events caused more than 800,000 deaths and affected about 262 million people from 1900–2013 [
7]. Gautam [
8] and Shiferaw et al. [
9] have reported that 382 dry spells between 1960 and 2006 affected 326 million people in Africa. Furthermore, a very severe drought in Africa during 2010–11 resulted in massive migration, extreme hunger, and the mortality of more than 260,000 people [
10]. Henchiri et al. [
11] reported that in North and West African regions, severe drought events occurred in 2002, 2009, 2010, and 2016, though the severity and impact differed from one country to another. Shanahan et al. [
12] surmised that the severe drought experienced in the Sahel in the 1970s was not uncommon in the context of the last three millennia, and proposed that the monsoon is capable of triggering more extended and severe droughts, which the world will experience in the future. The driest years have become more frequent, now occurring at shorter intervals, and the geographic extent of drought has also increased in West Africa according to Gautier et al. [
13]. Oguntunde et al. [
14] studied the characteristics of drought and projected the effects of future climate change on drought in West Africa between 1986 and 2100. They reported that the historical pattern of drought was consistent with previous studies conducted over most parts of West Africa, and predicted that an increase in drought intensity and frequency can be expected.
Mauritania, along with various countries in the Sahel, was dramatically impacted by severe droughts during the 2010–11 rainy seasons, which resulted in poor harvests, loss of livestock, and high food prices [
9,
15,
16]. Winkler et al. [
17] studied the droughts affecting agriculture in Africa between 2000–16, finding that during La Niña 2010–11, large cropland areas in Somalia (88%), Sudan (64%), and South Sudan (51%) were affected by severe to extreme droughts during the growing seasons. In addition, the study of Elagib and Elhang [
18] from the 1940s to 2008 showed several multi-year droughts to have occurred from the 1970s onward in Sudan. Furthermore, Gargouri et al. [
19] described how Algeria and Tunisia experienced severe drought during 1999 and 2002. Touchan et al. [
20] observed that over the last 1000 years, droughts have occurred every 20 years or so, on average, which could last for two to four successive years in the Mediterranean regions. Numerous investigations, meanwhile, have shown that the frequency of having one dry year is high for Algeria, Tunisia, and Morocco, and the frequency of two or more successive drought years is generally high in the south, moderate in the middle, and low in the north of the continent [
21,
22,
23]. Dry spell phases can affect one or various areas, and their duration can last from one month or season, extending to one year or more [
24].
These enumerations of the drought impact in recent years indicate that drought is a recurring, worldwide natural phenomenon, of which the related losses rise day by day [
25,
26,
27]. In research, remote sensing data and methods are critical tools for studying droughts’ underlying drivers. Numerous studies over the last few decades have investigated drought based on their magnitude and severity using different indices, such as multivariable linear regression with composite drought indices (MCDIs) by Liu et al. [
28]; optimized vegetation and meteorological drought indices (OVDI and OMDI) by Hao et al. [
29]; the US drought monitor (USDM) by Svoboda et al. [
30]; the reclamation drought index (RDI) by Weghorst [
31]; the standardized precipitation index (SPI) by McKee et al. [
32]; the Palmer drought severity index (PDSI) by Palmer [
33]; the decile index (DI) by Gibbs and Maher [
34]. The SPI was used to study meteorological drought, but this tool can be applied at various timescales to categorize diverse types of drought [
35]. Long timescales designate groundwater drought, medium timescales designate hydrological drought, and short timescales are linked to soil moisture and agricultural drought [
36].
Understanding the determinants of dry spells’ occurrence is significant in forecasting future events, which acts to prevent adverse effects on the environment [
37]. In many regions, observed recurrent droughts are linked with the phenomenon of the El Niño–Southern Oscillation (ENSO) [
38,
39]. The fundamental climate conditions that cause dry spells are high-pressure systems at a huge scale across a region (over an extended period of low-pressure forecast), rain-bearing frontal systems moving into the zone, or elevated convectional conditions that persevere [
40,
41]. The adjustments in the overarching climate dynamics that trigger these situations are still ineffectively comprehended [
42]. These teleconnections are characterized as repeating and persistent huge-scale patterns of circulation anomalies and pressure across large areas, or even more basically, as atmospheric interactions between usually isolated areas of the ground [
38]. The teleconnections can last from weeks to months and may appear for numerous successive years, meaning that they could play a significant role in interdecadal and interannual atmospheric variability. Since they influence precipitation, temperature, jet stream location, storm tracks, and intensity, teleconnections are frequently held accountable for unusual climate patterns across regions [
40,
41,
43]. Different teleconnections are found around the globe, and specific indices often characterize their strengths and phases. The main teleconnections of concern in this study were the Mediterranean Oscillation Index (MOI), Southern Oscillation Index (SOI), and North Atlantic Oscillation Index (NAOI), obtained from the Climate Research Unit (CRU).
In this context, ENSO is related to regional climate variability and associated droughts over large parts of the African continent. In general, Africa is the hottest and most water-scarce continent on earth [
17]. The Mediterranean climate is characterized as a mid-latitude temperate climate with a dry summer season. Precipitation has a distinct yearly cycle, with low precipitation in the summer season, as well as a spatial gradient, with values dropping toward the south [
44]. The high variability of the Mediterranean climate at seasonal and inter-annual scales is caused by the transitional situation between temperate, cold mild-latitudes and the tropics, resulting in significant circulation changes between winter and summer, as well as the association with several large-scale atmospheric oscillations/teleconnection patterns [
44].
The climate of West Africa, meanwhile, is influenced by the interaction of two air masses, the effect of which fluctuates during the year due to the north-south movement of the Intertropical Convergence Zone (ITCZ) [
17]. From November to February, dusty Harmattan winds blow throughout most of West Africa as a result of hot, dry continental air masses coming from a high-pressure system above the Sahara desert. Annual monsoon rains are brought by moist equatorial air masses originating over the Atlantic Ocean in the summer [
45]. As a result of these interacting air masses, West Africa’s precipitation regime is defined by latitudinal belts of decreasing rainfall and the wet season length. Not only the scarcity of rainfall but also its variability and unpredictability become more significant with increasing latitude. As a result, rainfall variability is great from year to year, ranging from 10 to 20% in coastal regions and up to more than 40% in the northern Sahel [
46]. Therefore, drought is considered a recurrent phenomenon in North and West African regions.
The Mediterranean droughts, particularly those that occur during the wet season, can have a significant impact on water resources by lowering groundwater levels and the amount of water available in dams and reservoirs [
17,
47,
48,
49]. Meanwhile, in semiarid West Africa, normal rainfall is rare and rainfall is biased to dryness, with a few big rainfall years offset by a larger number of below-average rainfall years [
50,
51]. Therefore, with rainfall as the limiting factor for farming and many countries strongly relying on rain-fed agriculture, droughts affect natural ecosystems, crop production, and the food supply, and may have severe socioeconomic impacts [
52,
53]. What is more, severe dry episodes in Africa have often been linked to the effects of the El Niño–Southern Oscillation (ENSO), leading to regional precipitation and temperature anomalies around the globe [
54]. Considering the recent drought events of recorded history, and the devastating effects of drought on agriculture and food security over large parts of Africa, monitoring and understanding ENSO-related droughts in North and West Africa is a major concern for implementing measures of adaption to drought hazards.
In this study, meteorological droughts are analyzed using the SPI at 1–12-month timescales, to assess the dry and wet spells from 1982 to 2018 over North and West Africa. Using the joint probability distribution function (JPDF), the drought return periods were calculated based on their characteristics. MOI, NAOI, and SOI data from the CRU (1982–2018) were used to examine the ENSO-drought relationship over the study area. The result of this study can be considered when interrogating future drought variations in comparison with the historical period.
4. Discussion
The most widely used drought indicator is the actual precipitation, represented as a percentage variation from normal (or long-term average), although it has limited use/reliability for regional comparison due to its reliance on the mean [
73]. According to Ye et al. [
74], the SPI reflects a deviation from the mean and is thus expressed as a normalized index in time and space in standard deviation units. The deviation from the mean is a probabilistic indicator of the severity of the wetness or drought that may be used to estimate risk. Given that the SPI is a statistical approach, it was preferable to use data from as far back as 1982 in this study. Long records provide more trustworthy statistics for the SPI. As a result of the availability of such data records, the SPI has gained traction as a potential drought indicator in recent years, allowing for comparisons across different precipitation zones [
73,
74].
The results of this study revealed that extremely low or extremely high precipitation was linked with extremely low or extremely high SPI values. When the precipitation was very low or very high, SPI readings accurately predicted the dryness or wetness.
Table 2 demonstrates that all periods with dry spells had low/negative anomaly and SPI values, with the driest being 2010–2011 (2.37) followed by 2009–2010 (1.76). Similarly, wet spell periods showed positive anomaly and SPI values, with the wettest periods being 2014–2015 (1.51) and 2015–2016 (1.23). The findings of this investigation are consistent with the SPI classifications of McKee et al. [
32]. Our results are also consistent with Henchiri et al. [
11], who evaluated the spatiotemporal patterns of drought and its impact on vegetation in North and West Africa, finding that 2002, 2009, 2010, and 2016 were the driest years, and 2014 and 2015 were the wettest years. Furthermore, Ghoneim et al. [
75] analyzed vegetation drought in North Africa (Tunisia) and identified 2002 as the driest year. Moreover, SPI analysis at 1, 3, 6, and 12–month timescales showed that shorter timescales have large temporal variability in dry and wet periods, but longer timescales (12 months) have a much lower frequency of dry and wet periods (
Figure 4). Furthermore, drought characteristic analysis showed that years of higher drought magnitude increased when the duration of drought was longer, and vice versa (see
Table 3 and
Figure 6). Also, the severity of drought might differ in a specific region in different years (see
Figure 7), which confirms the findings of the study of Orimoloye et al. [
14]. They mentioned that the Sahel experiences severe drought conditions with a significantly greater water deficiency than elsewhere, especially during the late dry seasons. The period of 2001 to 2019, during late dry seasons, showed severe to extreme drought conditions, while the region observed mild droughts, such as in 2001 and 2003–2018, where the region observed no to moderate drought events during the wet seasons. Additionally, numerous studies over arid regions, such as those of Kim et al. [
62], Kalisa et al. [
57], and Mesbahzadeh et al. [
76], have mentioned that the likelihood of drought is higher when the severity is lower, and that such a drought happens at a short timescale. Simultaneously, severe drought conditions take many years to repeat themselves, as was confirmed by the results of the JPDF and joint return years analysis in our study (see
Figure 8 and
Figure 9).
The findings of this study show that drought characteristics analysis (magnitude, intensity, and duration) using SPI can be applied to accurately measure the drought intensity in regions like North and West Africa, where drought sensitivity and low precipitation are common.
The SPI–12 and precipitation anomalies (
Appendix A,
Table A1,
Table A2,
Table A3 and
Table A4), the Mann-Kendall trend and significance level of 1–12-month SPI (
Table 4), and the Mann-Kendall trend and significance level of precipitation (
Table 5) demonstrate varied findings, both spatially and temporally, over North and West African countries. For example, a country may have the same drought level (SPI), but the precipitation anomaly values may differ (
Appendix A,
Table A1,
Table A2,
Table A3 and
Table A4). The drought of 2010–11 was worst in countries like Mauritania, Senegal, Mali, Niger, Sudan, Guinea, Burkina Faso, and Chad. From 2002–03, Algeria, Tunisia, Morocco, and Libya experienced severe drought conditions. Also, from 2000–01, Morocco and Libya experienced severe drought episodes (
Appendix A,
Table A1,
Table A2,
Table A3 and
Table A4).
Table 4 reveals that out of 17 countries, the tested models of SPI indicated that SPI–12, SPI–3, and SPI–1showed significant trends in Algeria, Tunisia, Mali, and Cote d’Ivoire with Sen’s slope (Kendall’s tau) values of 0.021 (0.156), 0.009 (0.127), and 0.006 (0.102); 0.007 (0.054), 0.007 (0.127), and 0.006 (0.187); 0.013 (0.095), 0.012 (0.159), and 0.009 (0.235); and 0.010 (0.076), 0.008 (0.105), and 0.009 (0.130), respectively. Also, the tested models of SPI indicated that SPI–12 showed significant trends in Burkina Faso and Niger with Sen’s slope (Kendall’s tau) values of 0.008 (0.070) and 0.007 (0.048), respectively. The results in
Table 5 illustrate positive and negative precipitation trends across North and West African countries. The tested models of precipitation showed significant trends in Algeria, Tunisia, Mali, Sudan, Burkina Faso, and Cote d’Ivoire with Sen’s slope (Kendall’s tau) values of 1.1375 (0.156), 0.637 (0.054), 1.352 (0.124), 0.087 (0.019), 0.619 (0.048), and 1.73 (0.07), respectively. Furthermore,
Table 5 shows that most countries suffered oscillations between dry and wet conditions, with a few countries becoming increasingly wet and others becoming increasingly dry. There was no discernible trend in precipitation at a regional scale. During the research period, there was no substantial change in the annual rainy season’s precipitation. We used SPI to study precipitation, to address potential changes in precipitation extremes, because there was no yearly trend in precipitation amount.
Due to the diverse plant varieties over the study area, which have variable water storage capabilities, a temporal lag was expected [
77]. The humid areas of various ports of West Africa (with mostly dense forests), as stated by Henchiri et al. [
11], are projected to have the largest time lag. This is because, according to McDowell et al. [
78], forests have the greatest capacity for water retention, with deeper roots to tap groundwater. Arid and semi-arid regions such as Sudan, Chad, Mali, Niger, Mauritania, Libya, Algeria, and Egypt, on the other hand, are primarily covered by grasslands and have a shorter time lag due to grasslands’ lower water retention capacity. The north parts of Algeria, Tunisia, Morocco, Libya, and Egypt are sub-humid areas covered by croplands. Croplands’ water storage capacity is estimated to be comparable to, if not lower than, that of grasslands. Moreover, artificial irrigation, according to Grünzweig et al. [
79], might change the time lag for irrigated agricultural zones. As a result, semi-arid areas are likely to have a temporal lag equivalent to or longer than dry areas [
80]. This pattern closely resembles the study’s findings, as illustrated in
Appendix A Table A1,
Table A2,
Table A3 and
Table A4,
Table 5, and
Figure 4,
Figure 6 and
Figure 7.
In terms of the ENSO-drought relationship over the study region, we sought to better understand the mechanism that drives drought and predict its variability, to enhance early warning and disaster risk management. We used the MOI, NAOI, and SOI, which displayed the La Niña, El Niño, and neutral conditions for various months of 1982–2018. For the MOI, La Niña was noted from November to February, and El Niño was detected from June to August in some years. The mean magnitude of SPI at different time scales was very similar during the neutral years for MOI, and the mean duration was between two and five years.
For the NAOI, the most noticeable La Niña years were 2002–03 and 2010–11, and for El Niño, 1991–92, 2014–15, and 2015–16 during autumn (SON) and winter (DJF), a period that concurs with the increased precipitation in northern regions. For NAOI during the neutral years, the mean magnitude was very similar for SPI at 1–12 months’ timescale, and the mean duration was similar for SPI–12, SPI–6, and SPI–3. For La Niña years, the mean magnitude and mean duration for SPI–1, SPI–3, and SPI–6 were similar, and in El Niño years, the mean magnitude and mean duration were similar for SPI–12, SPI–6, and SPI–3. These results with the spatial pattern of SPI–12 revealed that drought conditions could occur during La Niña years and wet conditions during El Niño years in many regions affected by the NAOI like Morocco, Algeria, and the sub-Saharan countries (
Figure 4,
Figure 12 and
Figure 13). This result clarifies that there is a direct connection between drought and the NAOI over these countries, which is in agreement with the work of Hurrell [
81] and Osborn et al. [
82], who mentioned that the North Atlantic Oscillation (NAO) is one of the main modes of variability of the northern hemisphere’s atmosphere. The NAO is especially important in winter when it exerts robust control over the northern hemisphere’s climate. Osborn [
83] also reported that this season could be subject to intense interdecadal variability; in winter, the difference of the normalized sea level pressure between Southwest Iceland and Gibraltar is a useful index of the strength of the NAOI. Furthermore, Mariotti et al. [
84,
85] found that averaged rainfall over the western Mediterranean is significantly correlated with ENSO variability in autumn, with the trend opposite to that found in spring.
For the SOI, the most noticeable La Niña years were 1986–87, 1991–92, 1997–98, 2002–03, and 2009–10, and the El Niño years were 1998–99, 2000–01, and 2007–08. The 1–12 month SPI revealed that for the SOI, the mean magnitude and duration were very similar during neutral, La Niña, and El Niño years. Comparison of this result with the spatial pattern of SPI–12 revealed that drought conditions could occur during La Niña years in many regions affected by the SOI like Guinea, Ghana, Sierra Leone, Mali, Cote d’Ivoire, Burkina Faso, Niger, and Nigeria (
Figure 4,
Figure 14 and
Figure 15). Our result was affirmed by Ogunjo et al. [
51]; they investigated the impact of large-scale ocean oscillation indices—the SOI, NAO and Pacific Decadal Oscillation (PDO)—on drought over West Africa. They found that the SOI showed a predominantly positive correlation with drought over the West African region, while PDO and NAO showed a negative correlation. Moreover, Addi et al. [
86] studied the impact of large-scale climate indices on the meteorological drought of coastal Ghana (West Africa). They found that the SPI and ENSO led to moderate to severe drought during the dry seasons, meaning they have great potential for seasonal drought prediction over coastal Ghana. This conclusion demonstrates that drought in these regions can be linked to the SOI. The trend in the ENSO originating in both the Pacific and Indian Oceans influences the regional climate of West Africa. This affirms that the global phenomenon’s apparition impacts weather conditions, and mainly those in West Africa, as confirmed by Egbuawa et al. [
87] and Adeniyi et al. [
88].
5. Conclusions
There is a consensus on the increase in droughts over the past decades, nor on future climate scenarios, for most regions of Africa. Recent studies have made significant progress in understanding drought in West and North African regions, as well as the effects of climate change, but further research is needed due to the uncertainty remaining in regional climate responses. This could be addressed by recent advances in climate modelling, which take advantage of increased spatiotemporal resolutions and a better quality of observations. In the current study, the SPI index was used to effectively describe the meteorological drought over North and West African regions from 1982 to 2018. The result for 36 years showed 13 dry years and 23 wet years. The SPI analysis at different timescales revealed a higher temporal variability in wet and dry periods for short timescales, while for long timescales, it was lower. The drought characteristics also showed that years of higher drought magnitude increased when the duration was longer (and vice versa), and the severity of drought differed across the study area over the different study years. In terms of the ENSO-drought relationship, the NAOI showed that the mean drought characteristics, duration, and magnitude for SPI–1, SPI–3, and SPI–6 were similar in La Niña years, while the mean drought characteristics for SPI–12, SPI–6, and SPI–3 coincided with El Niño years. The SOI showed that the mean magnitude and duration were very similar during La Niña and El Niño years at various timescales. The NAOI and SOI with the spatial pattern of SPI–12 revealed that drought conditions could occur in many regions. In Morocco, Algeria, and the sub-Saharan countries, the result clarified a direct link between the NAOI and drought in these countries. The findings of this study also exposed how drought is linked with the SOI in Guinea, Ghana, Sierra Leone, Mali, Cote d’Ivoire, Burkina Faso, Niger, and Nigeria.
The SPI was an applicable and suitable index for drought monitoring over the study region as it offered drought analysis at various timescales. This research might aid in improving our understanding of drought characteristics and return years, and their association with the ENSO over the study area, which will be useful for monitoring droughts in an integrated manner. Moreover, this study offers policymakers essential information that is prerequisite to local adaptation, increased mitigation measures, and resilience in the face of a vulnerable ecoclimatic system, brought on by constant climate change in the study area. For improved understanding of the drought processes related to climate change, a shift from index-based analysis to impact-based research is likely required. Adaptation to forthcoming climate changes will present a huge challenge for the region, and this necessitates a comprehensive assessment of droughts that includes a realistic representation of the water available in soils, drought propagation, feedback from vegetation cover, and human influence during these events.