Global warming has increased the risk of meteorological drought and associated hazards. Based on daily data from 35 meteorological stations in the Songhua River Basin (SRB) collected from 1960 to 2019, this study applied the standardised precipitation evapotranspiration index (SPEI) and used the ensemble empirical mode decomposition (EEMD) method and Pettitt's mutation test to perform a partitioned segmentation analysis of the multi-temporal and spatial variations in the meteorological droughts affecting the basin in terms of frequency and intensity, and discussed the relationship between the atmospheric circulation index and meteorological drought. The results showed that the overall meteorological drought trends shifted from a drought to a humid trend from 1960 to 2019. The drought in the basin had periods of 3, 6.7, 15, and 30 years, with mutation points in 1968, 1980, 1997, and 2012. The drought trend in Regions I and IV of the entire basin was enhanced, while that in Regions II, III, and V was weakened. Drought in the basin was strongly influenced by the Arctic Oscillation (AO) and Southern Oscillation Index (SOI).

  • The SRB shifted from a drought trend to a wet trend from 1960 to 2019.

  • High-frequency and high-intensity drought areas are mainly distributed in Regions I and IV.

  • Drought in the basin is greatly influenced by AO and SOI.

Droughts are natural disasters caused by uneven spatial and temporal distribution of precipitation, increased evapotranspiration, and inadequate water supply (Augustine & Lin 2023) and characterised by long duration, high occurrence frequency, and wide impact range (Rahman & Lateh 2016; Tong et al. 2017). Droughts can be categorised as meteorological, hydrological, agricultural, and socio-economic, with meteorological droughts representing one of the drivers of other forms of drought (Gumus et al. 2023). The study points out that the frequency and intensity of meteorological drought events caused by global warming will continue to increase in the future (Fung et al. 2020). Therefore, in the context of global climate change, it is of great significance to investigate the evolution of meteorological droughts at the regional scale to achieve sustainable development.

Given the difficulty of quantifying the intensity and frequency of droughts and accurately monitoring changes in these factors, scholars worldwide have developed a variety of drought indicators to meet the needs of research and applications in different fields (Wondimu et al. 2023; Yang et al. 2023). Among them, the Palmer drought severity index (PDSI; Palmer 1965) is based on the principle of water balance and considers the effects of factors such as the supply and demand of actual moisture on meteorological drought; however, it is not spatially comparable. The standardised precipitation index (SPI; McKee et al. 1993) only considers changes in precipitation and ignores changes in evapotranspiration caused by temperature rise in the meteorological drought, which represents a limitation for studies on drought in the context of climate warming. In addition, the standardised precipitation evapotranspiration index (SPEI; Vicente-Serrano et al. 2009) combines the advantages of the PDSI and SPI indices and considers the effects of temperature changes and water balance on drought while calculating the multi-scale characteristics of drought. The SPEI has been widely applied in the study of meteorological drought. Studies in Bangladesh (Mohammad et al. 2022) and Sichuan Province, China (Liu et al. 2021) showed that the SPEI has better applicability than the SPI, and research in the Java Island region (Suroso et al. 2021) and northeastern China (Shen et al. 2017) revealed that the SPEI can accurately characterise drought events.

In recent years, most studies on meteorological drought have used methods such as linear fitting or wavelet transform to analyse the associated change trends, and these methods assume the linearity and stationarity of the time series (Tong et al. 2017; Ye et al. 2019). However, the inherent non-linear characteristics of meteorological factors will cause deficiencies in the linear fitting of climate element time series trends, and studies have shown that changes in meteorological drought are affected by the non-linear characteristics of climate factors (Song et al. 2020; Wu et al. 2023). As one of the most recent methods developed to analyse the trends and cycles of time series, the Ensemble Empirical Mode Decomposition (EEMD; Huang & Wu 2008) method can determine the inherent trends of non-linear and non-stationary time series and determine the inherent trend of non-linear and non-stationary time series during meteorological drought (Li et al. 2015; Liu et al. 2020) and precipitation changes (Guo et al. 2016). Thus, it has been widely used in trend and cycle studies.

In addition to being affected by regional environmental factors, drought events are also impacted by large-scale atmospheric and ocean circulation parameters (Li et al. 2015; Manzano et al. 2019). Atmospheric circulation factors can affect the mass, heat, and momentum in the atmosphere, thereby causing climate anomalies (Wang et al. 2020). Previous research has shown that the Pacific Decadal Oscillation (PDO), North Atlantic Oscillation (NAO), Arctic Oscillation (AO), and Southern Oscillation Index (SOI) are strongly correlated with meteorological drought in the Liaohe River Basin in China (Chen et al. 2023a); precipitation in northeastern India is closely related to the Atlantic Multidecadal Oscillation (AMO), El Niño Southern Oscillation (ENSO), and PDO (Singh et al. 2020); and precipitation in Northeastern China is affected by the NAO and PDO, and NAO and PDO in turn affect drought (Zeng et al. 2019). Therefore, the atmospheric circulation index may have a direct or indirect impact on drought, and it is important to analyse its intrinsic relationship with drought events.

The Songhua River Basin (SRB) is located in northeastern China in a temperate continental semi-humid and semi-arid monsoon climate zone, and it represents one of the seven major river basins of China, and it is an important grain-producing area and commercial grain production base in China (Yu et al. 2023). As one of the regions in China most affected by global climate change, the SRB experiences frequent droughts (Ye et al. 2019). The risk of drought in SRB will increase in the future under the continued threat of global warming (Abrar et al. 2018, 2019; Wu & Zhang 2018). Therefore, studying the evolution of meteorological drought in SRB is important for developing adaptation strategies to reduce drought losses. However, the detailed study of meteorological droughts in each subregion of the basin has not yet been carried out, and the non-linear trend and periodical characteristics of meteorological droughts as a result of climate factor fluctuations are not yet clear, and the influence of atmospheric circulation factors on meteorological droughts in the basin is still not clear.

This study focuses on SPEI time series data and uses the EEMD method and Pettit mutation to analyse the trends, periods, and mutation characteristics of the SPEI data. Moreover, the spatial distribution of droughts at different time scales is assessed based on the drought frequency and intensity, and the relationship between drought events and circulation indices is discussed. This study provides insights for performing detailed assessments of drought in the SRB and conducting effective drought monitoring.

Study area

The SRB is located between 119°52′–132°31′ E and 41°42′–51°38′ N and spans the three provinces of Inner Mongolia, Heilongjiang, and Jilin. The basin is 1,070 km wide from north to south and 920 km long from east to west and has a total watershed area of 55.68 × 104 km2. The basin has a substantial seasonal temperature difference, with the multi-year average temperature ranging from 3–5 °C. The spatial and temporal distribution of precipitation in the basin is relatively uneven, and the average annual precipitation is approximately 500 mm. Precipitation is mainly concentrated in June to September, accounting for approximately 60–80% of the annual precipitation. The SRB was divided into five subregions according to differences in topography and geomorphology, considering the ecological environment and socio-economic factors as shown in Supplementary Figure S1(b) (Zhang et al. 2019). The main drought trends in the basin were analysed on a subregional basis, which is important for basin zonal drought variability and multi-regional joint studies. Supplementary Figure S1(a) shows the location of the SRB and its elevation is shown in Supplementary Figure S1(c).

Data sources and processing

Meteorological data for the SRB from 1960 to 2019 were derived from the China Surface Climatological Data Daily Value Dataset (V3.0) (https://data.cma.cn/) and include the daily average air temperature, maximum air temperature, minimum air temperature, daily rainfall, latitude, and longitude. The data were processed as follows. Station data included in the study were no less than 60 years old, and stations with more than 5% missing data or more than 30 consecutive days without data collection were excluded. Data interpolation was conducted to supplement the data when part of the data was missing. Data from 35 meteorological stations in the SRB were obtained and used for calculations and analyses. The atmospheric circulation data from 1960 to 2019 used in this paper have a temporal resolution of monthly scale, and the corresponding seasonal and annual scale data were calculated by averaging the monthly scale data and analysed for correlation with the SPEI of the same period, including the AO, Indian Ocean Dipole (IOD), SOI, and Western Pacific Remote Correlation (WP) (http://www.noaa.gov/). The underlying spatial data were derived from the Geospatial Data Cloud 30 × 30 m resolution digital elevation model (https://www.gscloud.cn/) and National Zone Boundary Vector Data (https://www.craes.cn/).

Methods

Standardised precipitation evapotranspiration index

The SPEI is an indicator used to assess the probability of the difference between precipitation and evapotranspiration in a given period (Vicente-Serrano et al. 2009). It considers the response of precipitation and evapotranspiration to drought and is suitable for monitoring and assessing droughts at different time scales in semi-arid and semi-humid regions. The specific calculation procedure is described in Liu et al. (2020). The four seasons were divided according to the meteorological seasons, meaning that March–May was spring; June–August was summer; September–November was autumn; and December–February was winter. Drought categories were classified based on relevant studies as shown in Supplementary Table S1 (Wang et al. 2018).

Ensemble empirical mode decomposition method

The EEMD is a signal processing and data analysis method (Huang & Wu 2008) developed based on empirical mode decomposition (EMD) (Huang et al. 1998; Wu & Huang 2004). It addresses the problems of modal aliasing and instability in the application of the EMD method and is suitable for analysis of non-smooth and non-linear time series as an adaptive non-linear signal decomposition method. This method mainly expresses the temporal distribution of the data by extracting the intrinsically correlated energy of the time scale and generating a set of intrinsic mode functions (IMFs) and residual (R) (Wu & Huang 2011). Also, all conclusions of this study are based on this non-linear trend of the meteorological drought after EEMD decomposition.

The specific procedures of EEMD can be summarised as follows:

  • Step 1: Input the target data as the original signal .

  • Step 2: Set the EEMD parameters, including the noise standard deviation , number of realizations , and maximum number of sifting iterations allowed .

  • Step 3: Conduct the decomposition. Add a normally distributed white noise series with finite amplitude to the given signal , and reconstruct a new set of series using Equation (1):
    (1)
  • Step 4: Decompose into n levels of IMFs and a trend term for the decomposition by EMD using Equation (2):
    (2)
    where is the IMF after the decomposition.
  • Step 5: Repeat steps 2 and 3 with different white noise series until the maximum number of realizations is achieved for i.

  • Step 6: Obtain IMFs by calculating the ensemble means of the corresponding IMFs to eliminate mode mixing. The final results are given by Equations (3) and (4):
    (3)
    (4)

where is the IMF, and is the trend term.

Pettitt's mutation test

Pettitt's mutation test is a non-parametric statistical test commonly used to analyse the mutation points in a time series. It does not require sample hypothesis testing, it is suitable for a variety of time series types, and it is widely used in meteorology, environment, and finance applications, among others. The calculation process is described in Pettitt (1981). Owing to the uncertainty of meteorological changes and human activities, there may be more than one mutation point in the sequence that needs to be tested several times (Li et al. 2014a). The specific steps are as follows. The first level mutation point in the sequence should be detected using the Pettitt's method. According to the first level mutation point found, the original sequence should then be split into two, before and after the mutation of the two segments of the sequence before being tested again. If there is no new mutation point, this means that all potential mutation points have been identified. This is then used to determine the sequence segments. If a mutation point remains, these steps are repeated.

Drought indicators

Drought frequency is the ratio of the number of years with drought events during the study period to the total number of years during the study period (Wang et al. 2022). The calculation formula is as follows:
(5)
where P is the frequency of drought, n is the number of years with drought during the study period, and m is the total number of years during the study period.
Drought intensity is the multi-year average of the absolute value of SPEI when there is a drought event (Wang et al. 2018). It indicates the severity of the drought occurrence and is calculated as follows:
(6)
where I represents drought intensity, n represents the number of drought events during the study period, and represents the SPEI value at the time of drought during the study period.

Temporal characterisation of drought

Annual-scale SPEI characterisation

We calculated SPEI values on an annual scale for the SRB from 1960 to 2019 and analysed their periods and trends using the EEMD method. As shown in Figure 1, the SPEI value is less than −0.5, which means that drought has occurred for a total of 20 years, and the SPEI reached its lowest value of −2.13 in 2001, representing an extreme drought level. The SPEI values were decomposed to obtain four IMF components (IMF1–4) and the trend item R. Each of these IMF components successively reflects the oscillatory characteristics inherent in the original data at different scales from high to low frequencies. IMF1 and IMF2 represent the periodic variations of SPEI on the annual scale, IMF3 and IMF4 represent the periodic variations on the decadal scale, IMF1 and IMF2 represent the characteristics of SPEI variations at different frequencies, IMF1 frequency is higher than that of IMF2, and IMF3 frequency is higher than that of IMF4. Relatively stable quasi-periodic variations show non-uniform variations of different intensities over time within the same study period. The trend item R denotes the non-linear trend of the SPEI over time, representing its inherent long-term trend. The trend item R showed non-linear and non-stationary characteristics, with a decreasing trend between 1960 and 1990, and an increasing trend between 1990 and 2019. The overall trend of trend item R indicates that the basin experienced a clear transition from dry to wet conditions around 1990.
Figure 1

Variation trend of the annual-scale SPEI value and EEMD decomposition components in the SRB from 1960 to 2019.

Figure 1

Variation trend of the annual-scale SPEI value and EEMD decomposition components in the SRB from 1960 to 2019.

Close modal

To further resolve the oscillations of different feature scales present in the original data, the variance contribution ratio and the correlation coefficient of each IMF component was calculated using the Fast Fourier Transform method. The variance contribution ratio is the extent to which each intrinsic modal function (IMF) of the original SPEI series contributes to the total variance of the original series during the EEMD. It is calculated by comparing the ratio of the variance of each IMF to the variance of the original series, the variance contribution ratio can be used to measure the importance of each IMF in explaining the variability of the original series. The correlation coefficient is a statistical measure of the strength of correlation between each IMF of the original SPEI sequence and the original sequence during the EEMD process, and by analysing the correlation between the IMF components and the original sequence, it is possible to identify those components that contain key information about the original sequence as shown in Table 1. The main periods of IMF1, IMF2, IMF3, and IMF4 were 3, 6.7, 15, and 30 years, respectively. The 3-year period of the IMF1 component had the largest variance contribution of 45.92%, with a correlation coefficient of 0.696. The IMF2, IMF3, and IMF4 components had variance contributions of 13.8, 10.5, and 23.89%, respectively, with correlation coefficients of 0.391, 0.229, and 0.501, which were significant. As shown by the variance contributions of the individual components, annual oscillations dominated the annual-scale SPEI variations, which were mainly determined by IMF1, with a main period of 3 years.

Table 1

Characteristics of each IMF component of the EEMD decomposition of the annual-scale SPEI value in the SRB from 1960 to 2019

Statistics IndexIMF1IMF2IMF3IMF4
Period (Year) 6.7 15 30 
Contribution rate (%) 45.92 13.80 10.50 23.89 
Correlation coefficient 0.696** 0.391** 0.229* 0.501** 
Statistics IndexIMF1IMF2IMF3IMF4
Period (Year) 6.7 15 30 
Contribution rate (%) 45.92 13.80 10.50 23.89 
Correlation coefficient 0.696** 0.391** 0.229* 0.501** 

*Indicates the value at a 0.05 significance level.

**Indicates the value at a 0.01 significance level.

Seasonal-scale SPEI characterisation

Figure 2 illustrates the seasonal SPEI values for the SRB from 1960 to 2019 and the components derived from the decomposition. The spring SPEI showed the minimum value reaching −2.89, indicating an extreme drought level in 1963. Trend item R showed an overall non-linear upward trend, indicating that the catchment underwent a gradual wetting process in spring during the study period. The summer SPEI values showed that there was a total of 21 years of drought, with a minimum value of −2.01, occurring in 1997 at the extreme drought level and −1.73 occurring in 1965 at the severe drought level. Trend item R generally showed a decreasing, slow increasing, and then a decreasing drought trend. A total of 21 years of drought occurred in autumn, reaching a minimum value of −1.83 in 1978. This was a severe drought, and the trend term R showed a tendency to change first upward and then downward. A total of 18 years of drought occurred in winter, reaching a minimum value of −2.02 in 2018, which was at the level of extreme drought. Trend term R showed a slow and non-linear upward trend, indicating a tendency to alleviate winter drought in the basin during the study period.
Figure 2

Variation trend of the seasonal-scale SPEI value and EEMD decomposition components in the SRB from 1960 to 2019: (a) spring, (b) summer, (c) autumn, and (d) winter.

Figure 2

Variation trend of the seasonal-scale SPEI value and EEMD decomposition components in the SRB from 1960 to 2019: (a) spring, (b) summer, (c) autumn, and (d) winter.

Close modal

The period, variance contribution, and correlation coefficients of the components derived from the seasonal decomposition of the SPEI values are listed in Table 2. The spring SPEI values had 2.9- and 6-year periods in annual variability, with a higher percentage of variance contribution (54.77 and 36.71%, respectively). The decadal variability had 12- and 20-year periods. The main periods of the components of the summer SPEI values were 2.5 (71.96%), 5 (11.92%), 12, and 30 years, respectively. Autumn SPEI values had periods of 2.7 (71.19%) and 5.5 (14.07%) years in annual variability and 15 and 20 years in decadal variability. The main periods of the components of the winter SPEI values were 3 (54.14%), 6, 12, and 30 years (13.44%), respectively. The seasonal SPEI variations were determined by annual oscillations, and the main periods were dominated by the IMF1 component.

Table 2

Characteristics of each IMF component of the EEMD decomposition of the seasonal-scale SPEI value in the SRB from 1960 to 2019

TimescaleStatistics IndexIMF1IMF2IMF3IMF4
Spring Period (Year) 2.9 12 20 
Contribution rate (%) 54.77 36.71 17.47 1.01 
Correlation coefficient 0.711** 0.528** 0.254* 0.098 
Summer Period (Year) 2.5 12 30 
Contribution rate (%) 71.96 11.92 7.48 4.31 
Correlation coefficient 0.757** 0.490** 0.378** 0.196 
Autumn Period (Year) 2.7 5.5 15 20 
Contribution rate (%) 71.19 14.07 9.05 0.87 
Correlation coefficient 0.857** 0.470** 0.310** 0.082 
Winter Period (Year) 12 30 
Contribution rate (%) 54.14 13.36 2.62 13.44 
Correlation coefficient 0.815** 0.538** 0.264* 0.394** 
TimescaleStatistics IndexIMF1IMF2IMF3IMF4
Spring Period (Year) 2.9 12 20 
Contribution rate (%) 54.77 36.71 17.47 1.01 
Correlation coefficient 0.711** 0.528** 0.254* 0.098 
Summer Period (Year) 2.5 12 30 
Contribution rate (%) 71.96 11.92 7.48 4.31 
Correlation coefficient 0.757** 0.490** 0.378** 0.196 
Autumn Period (Year) 2.7 5.5 15 20 
Contribution rate (%) 71.19 14.07 9.05 0.87 
Correlation coefficient 0.857** 0.470** 0.310** 0.082 
Winter Period (Year) 12 30 
Contribution rate (%) 54.14 13.36 2.62 13.44 
Correlation coefficient 0.815** 0.538** 0.264* 0.394** 

*Indicates the value at a 0.05 significance level.

**Indicates the value at a 0.01 significance level.

Drought mutation detection based on the Pettitt method

The year of mutation of the annual SPEI sequence in the SRB was detected using the Pettitt mutation detection method. The study period was divided according to the year of mutation, and the results of the division are shown in Supplementary Figure S2. The years of mutation in the annual SPEI sequence were 1968, 1980, 1997, and 2012. Therefore, the study period was divided into five phases: 1960–1967, 1968–1979, 1980–1996, 1997–2011, and 2012–2019. The average SPEI values at each stage were 0.204, −0.607, 0.739, −0.490, and 0.782, respectively.

Subregion annual SPEI characterisation

As shown by the change in the SPEI trend term R for each subregion of the SRB from 1960 to 2019 (Figure 3), the SPEI series in Region I shows a general downward trend. The SPEI series in Region II showed a decreasing trend before 1980 and an increasing trend after 1980, with a transition from dry to wet conditions in 1980. The SPEI series for Regions III, IV, and V showed a decreasing trend before 1990 and an increasing trend after 1990, which is in line with the trend of the annual SPEI changes in the watershed.
Figure 3

Variation trend for SPEI in each subregion of SRB from 1960 to 2019: (a) Region I, (b) Region II, (c) Region III, (d) Region IV, and (e) Region V.

Figure 3

Variation trend for SPEI in each subregion of SRB from 1960 to 2019: (a) Region I, (b) Region II, (c) Region III, (d) Region IV, and (e) Region V.

Close modal

Spatial characterisation of drought

Spatial distribution of drought frequency

The drought frequency (P) of each subregion at different timescales for different study periods in the SRB is shown in Figure 4, and its spatial distribution is shown in Figure 5. From 1960 to 1967, the P for each season in the basin was 41.79, 18.57, 33.93, and 32.86%. Among them, the high-frequency area in spring was located in Region III, which showed a distribution pattern of low in the west and high in the east; that in summer was located in Region IV, and the distribution pattern was similar to that in spring; that in autumn was located in Region III; while that in winter was concentrated in Regions IV and V, with a wide range of overall drought. From 1968 to 1979, the P values for spring, summer, and autumn in the basin were 37.62, 46.43, and 34.52%, respectively, with the high-frequency zones concentrated in Region V. The P of winter was 26.43%, and the high-frequency region was Region IV, which showed a trend of low west and high east. From 1980 to 1996, the P values of the basin were 36.97, 21.85, 18.66, and 32.77% for the four seasons. Among them, the high-frequency area was located in Region III in spring, which showed a distribution pattern of high in the north and low in the south; in summer was concentrated in Region V; in autumn was located in Region IV; and in winter was concentrated in Region I, which showed a gradual decrease from west to east. Between 1997 and 2011, the P of the basin was 29.33% in spring and 52.57% in summer, with high-frequency areas concentrated in Region V; the P was 51.43% in autumn and concentrated in Region I, showing a distribution pattern higher in the west than in the east; and the P was 30.29% in winter and concentrated in Region II, with the trend being higher in the south than in the north. From 2012 to 2019, the P in spring and winter of the basin were 17.68 and 18.57%, respectively, with the high-frequency areas located in Region I, and the P in summer and autumn were 20.36 and 21.63%, respectively, with the high-frequency areas concentrated in Region IV.
Figure 4

Seasonal drought frequency during different research periods in the SRB from 1960 to 2019.

Figure 4

Seasonal drought frequency during different research periods in the SRB from 1960 to 2019.

Close modal
Figure 5

Seasonal spatial distribution of drought frequency in different research periods in the SRB from 1960 to 2019.

Figure 5

Seasonal spatial distribution of drought frequency in different research periods in the SRB from 1960 to 2019.

Close modal

Spatial distribution of drought intensity

The drought intensity (I) of each subregion at different timescales for different study periods in the SRB is shown in Figure 6, and the spatial distribution of the I is shown in Figure 7. From 1960 to 1967, the I for each season in the basin was 1.19, 0.95, 1.15, and 1.25. Among them, the high-value area in spring was located in Region IV, which showed a distribution pattern of high in the south and low in the north; that in summer was mainly located in Region I; that in autumn was concentrated in Region V, which presented a pattern of low in the west and high in the east; and that in winter was focused in Region I, with the centre being lower than the east and west. From 1968 to 1979, the I of the basin was 1.18 in spring, with high values located in Region V; that in summer was 1.12, with high values located in Region V; and that in autumn and winter was 1.23 and 1.01, respectively, with high-value areas concentrated in Region II. From 1980 to 1996, the I of the basin in spring was 1.14, and the high-value areas were located in Region IV; and that in summer, autumn, and winter was 1.13, 0.98, and 1.10, respectively, with high values concentrated in Region II. Between 1997 and 2011, the I of the basin in spring and summer was 1.14 and 1.10, respectively, with high values located in Region I, and that in autumn and winter was 1.20 and 1.15, respectively, with high values concentrated in Region IV. From 2012 to 2019, the I of the basin in spring was 1.17, and the high-value area was located in Region II, showing a distribution pattern of high in the west and low in the east; that in summer was 1.12, and the high-value area was located in Region I; that in autumn was 1.11, and the high-value area was located in Region I, and that in winter was 1.93, and the high-value area was located in Region V.
Figure 6

Seasonal drought intensity during different research periods in the SRB from 1960 to 2019.

Figure 6

Seasonal drought intensity during different research periods in the SRB from 1960 to 2019.

Close modal
Figure 7

Seasonal spatial distribution of drought intensity in different research periods in the SRB from 1960 to 2019.

Figure 7

Seasonal spatial distribution of drought intensity in different research periods in the SRB from 1960 to 2019.

Close modal

Spatial and temporal characteristics of drought

In terms of temporal changes in drought, there was a mitigating trend in the annual drought in the SRB from 1960 to 2019 (Ren & Dong 2022). This was consistent with the findings of this study. Ye et al. (2019) found that droughts in the SRB are affected by the combined effects of temperature and precipitation. A sudden change in temperature in the SRB occurred around 1990, while there were 7-, 14-, and 28-year periods of temperature change that coincided with the drought period in the basin (Li et al. 2014b). The entire basin has been continuously warming and becoming wetter, which may have contributed to this result (Yu et al. 2023). However, Li et al. (2020) concluded that there was a trend of enhanced autumn drought in the SRB, which is in contrast with the results of this study. This may be related to the study being conducted in different years and the drought indices selected.

In terms of the spatial distribution of drought, the drought-high-frequency region and the drought-intensity high-value region of the SRB from 1960 to 2019 were mainly distributed in Regions I and IV. This is similar to the results of Feng et al. (2016), who found that the drought area of the SRB was mainly distributed in the northeastern and southwestern regions. Song et al. (2015) found that precipitation indices, such as intense precipitation and annual precipitation indices in the SRB, showed an upward trend over time. However, the magnitude was relatively small, with a spatial trend of gradual decrease from the southeast to the northwest. Meanwhile, the sustained dry and wet period indices such as sustained dry days were mainly distributed in the western part of the SRB side by side, reflecting the reason for the more severe drought in Region I (Yu et al. 2023).

Relationship between SPEI and circulation indices

To further resolve the relationship between drought and circulation indices, four atmospheric circulation indices (AO, IOD, SOI, and WP) were selected for correlation analysis with annual SPEI values in the SRB. Table 3 presents the period of each component after the decomposition of each circulation index. The period of each circulation index for different components is the same as the period of the corresponding components of the annual SPEI. Therefore, the Pearson correlation analysis method could be used to analyse the correlation between the SPEI and circulation indices.

Table 3

Effect of periods (year) of AO, IOD, WO, and SOI on different components

IndexIMF1IMF2IMF3IMF4
AO 5.5 12 30 
IOD 3.2 5.5 12 30 
SOI 3.3 6.7 15 30 
WP 2.9 12 30 
IndexIMF1IMF2IMF3IMF4
AO 5.5 12 30 
IOD 3.2 5.5 12 30 
SOI 3.3 6.7 15 30 
WP 2.9 12 30 

Figure 8 shows the results of the correlation analysis of the components between the SPEI and AO, IOD, SOI, and WP at different time scales between 1960 and 2019 in the SRB. At the annual scale, the correlation among the SPEI and AO and WP were significant. When the AO was in a positive phase, the Siberian high-pressure was weakened, the monsoon was weak, and the temperature in the northeast was high, as well as having an impact on precipitation. This, in turn, affected the occurrence of drought events (Chen et al. 2023b). In spring, the correlation between the SPEI and each circulation index was relatively poor. The correlation with the AO, IOD, and SOI was more significant in summer when negative precipitation anomalies formed by the AO positive phase and the AO remote correlation formed an anomalous anticyclonic circulation over Lake Baikal. This enhanced the subsidence of the high-pressure ridges and their associated dynamics in Lake Baikal. The northerly winds located on the eastern side of the anticyclone attenuated the transport of water vapour from the south, which ultimately led to the persistence of spring–summer droughts in the northeast (Zeng et al. 2019). Meanwhile, the highly anomalous potential around Lake Baikal and the water vapour dispersion area in the northeast region triggered a precipitation deficit and high temperatures. This is one of the reasons for the frequent occurrence of spring and summer droughts in the northeast region (Hu et al. 2022). In autumn and winter, the correlation between SPEI, AO, and SOI was enhanced, and the correlation between IOD and WP was moderate. The correlation between the overall drought in the basin and the AO and SOI was also more pronounced. The correlation between the IMF3 and IMF4 components and the four circulation indices was more significant than that between the IMF1 and IMF2 components at certain timescales.
Figure 8

Component correlations between SPEI and AO, IOD, WP, and SOI at different time scales in the SRB from 1960 to 2019. (*Indicates the value at a 0.05 significance level, **Indicates the value at a 0.01 significance level).

Figure 8

Component correlations between SPEI and AO, IOD, WP, and SOI at different time scales in the SRB from 1960 to 2019. (*Indicates the value at a 0.05 significance level, **Indicates the value at a 0.01 significance level).

Close modal

Uncertainties and contributions

This multi-temporal study of spatiotemporal variations in drought in the SRB presented certain limitations. The selection of different indicators that represent meteorological droughts is likely to affect drought events in different ways. Ren & Dong (2022) selected the SPEI as a drought indicator to study the trend of meteorological drought in the SRB and concluded that there was a weakening drought trend. This contradicts the conclusion obtained by Wu & Zhang (2018), who selected the SPI as a drought indicator, thus highlighting the differences in the method of assessing trends and variations between the SPEI and SPI (Song et al. 2020). In addition to circulation indices, the impacts of various human activities on climate change have increased in recent years, and their impacts on drought events should be further explored (Zhao et al. 2023). Data over a longer time span are required to allow for a more accurate trend analysis of drought changes in the watershed and to test the veracity of the drought trend changes obtained in this study (El Kenawy et al. 2020). In addition, with global climate change, the prediction of future meteorological droughts is a research direction that cannot be ignored. Resolving these uncertainties may provide new insights for future research on the causes of drought events.

Moreover, the EEMD method used in this study describes fluctuations in the time series and accurately identifies features such as non-linear trends and periodic oscillations in the temporal variation of drought. This represents a considerable advantage in studies on the complex changes in drought (Feng & Su 2019). Meanwhile, by using factors such as the topography of the study area to divide the study area and mutation conditions to divide the drought time period to conduct a detailed multi-temporal study of drought events in the basin, we can more accurately identify the differentiation of drought changes in different regions at different times and deepen our understanding of spatial and temporal changes in drought in the basin (Luo et al. 2023). The results of the study have enriched the research results on meteorological drought in the SRB, and provide a basis for quantitative analysis of the spatial and temporal characteristics of meteorological drought in the basin. The results of the research can provide important references for the development of agriculture in the high-frequency and high-value drought regions of the basin, the scientific formulation of drought mitigation and planning, and the effective response to drought, which is of great significance in guaranteeing the food security of the country, and the promotion of the socio-economic-ecological system.

Based on data collected from 35 meteorological stations in the SRB from 1960 to 2019, this study used the SPEI as a drought indicator, applied the EEMD method to study the non-linear trend and cyclic changes of drought, and performed Pettitt's mutation test to analyse drought mutations that divide the study period. The temporal and spatial variations of droughts in the basin were analysed in terms of drought frequency and intensity. The correlations between the SPEI and the AO, IOD, SOI, and WP were analysed using Pearson's correlation analysis and cross-wavelet analysis, and the following conclusions were reached:

  • 1) The overall meteorological drought in the SRB during 1960–2019 showed periods of 3, 6.7, 15, and 30 years. There was a clear transition from drought to wetness around 1990. The SPEI time series had four mutation points based on Pettitt's mutation tests for 1968, 1980, 1997, and 2012.

  • 2) During the study period, drought in the SRB showed an increasing trend in Regions I and IV and a weakening trend in Regions II, III, and V. High-frequency and high-value drought regions were mainly distributed in the watershed in Regions I and IV. The frequency of spring droughts was higher in Regions I, II, and V. The frequency of autumn droughts was higher in Regions III and IV, and the value of drought intensity was higher in each subregion. The drought frequency and intensity in each subregion showed a trend of increasing and then decreasing.

  • 3) Annual-scale drought in the basin correlated more strongly with the AO and WP in spring and summer, mainly with the AO, IOD, and SOI. Drought in autumn and winter was mainly influenced by the AO and SOI.

This study analysed spatial and temporal variations in meteorological drought in the SRB based on the SPEI and examined the relationship between meteorological drought and circulation indices. The findings have highlighted the patterns of meteorological drought in the SRB and its causes, which can provide a reference for discussing drought events in other regions. However, a number of factors, including human activity, influence the formation of droughts, and future studies should further consider these additional aspects.

J.Xu: methodology, writing – original draft, formal analysis, conceptualisation. X.L.: formal analysis. J.Xue: formal analysis. X.D.: formal analysis. W.W. and G.W.: formal analysis. Q.Z.: writing – review and editing, conceptualisation, formal analysis.

This work is funded under the auspices of the National Natural Science Foundation of China (Grant Nos. 51909104, 51909105, and 41471160).

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

The authors declare there is no conflict.

Abrar
F. M.
,
Liu
D.
,
Fu
Q.
,
Muhammad
U.
,
Imran
K. M.
,
Faisal
B.
,
Li
T.
&
Cui
S.
2018
Stream flow variability and drought severity in the Songhua River Basin, Northeast China
.
Stochastic Environmental Research and Risk Assessment
32
(
5
),
1225
1242
.
https://doi.org/10.1007/s00477-017-1463-3.
Abrar
F. M.
,
Liu
D.
,
Fu
Q.
,
Faisal
B.
,
Tahir
A. A.
,
Li
M.
,
Imran
K. M.
,
Shoaib
M.
,
Li
T.
&
Cui
S.
2019
Multi-index drought characteristics in Songhua River basin, Northeast China
.
Climate Research
78
,
1
19
.
doi:10.3354/cr01558
.
Augustine
O. O.
&
Lin
Z.
2023
Trend and spatial-temporal variation of drought characteristics over equatorial East Africa during the last 120 years
.
Frontiers in Earth Science
10
,
101064940
.
https://doi.org/10.3389/feart.2022.1064940.
Chen
S.
,
Yu
H.
,
Ren
Y.
,
Zhou
J.
,
Luo
H.
,
Liu
C.
&
Gong
Y.
2023a
Research progress on the influence mechanism of climate anomalies in arid and semi-arid regions in China
.
Journal of Desert Research
43
(
3
),
21
35
.
https://doi.org/10.7522/j.issn.1000-694X.2022.00126.
Chen
Y.
,
Zhao
Q.
,
Ai
M.
,
Li
X.
&
Ran
P.
2023b
Spatio-temporal characteristics of meteorological drought in the Liaohe River Basin from 1959 to 2019
.
Water Resources and Hydropower Engineering
54
(
1
),
42
52
.
https://doi.org/10.13928/j.cnki.wrahe.2023.01.004.
El Kenawy
A. M.
,
Buloshia
A. A.
,
Al-Awadhia
T.
,
Nasiria
N. A.
,
Navarro-Serranoc
F.
,
Alhatrushia
S.
,
Robaad
S. M.
,
Domínguez-Castroe
F.
,
McCabef
M. F.
,
Schuwerackg
P. M.
,
López-Morenoc
J. I.
&
Vicente-Serranoc
S. M.
2020
Evidence for intensification of meteorological droughts in Oman over the past four decades
.
Atmospheric Research
246
,
105126
.
https://doi.org/10.1016/j.atmosres.2020.105126
.
Feng
K.
&
Su
X.
2019
Spatiotemporal characteristics of drought in the Heihe river basin based on the extreme-point symmetric mode decomposition method
.
International Journal of Disaster Risk Science
10
(
4
),
591
603
.
https://doi.org/10.1007/s13753-019-00241-1
.
Feng
B.
,
Zhang
G.
&
Li
F.
2016
Characteristics of seasonal meteorological drought and risk regionalization in Songhua river basin
.
Scientia Geographica Sinica
36
(
3
),
466
474
.
https://doi.org/10.13249/j.cnki.sgs.2016.03.019
.
Gumus
V.
,
Dinsever
L. D.
&
Avsaroglu
Y.
2023
Analysis of drought characteristics and trends during 1965–2020 in the Tigris River basin, Turkey
.
Theoretical and Applied Climatology
154
(
3–4
),
1871
1887
.
https://doi.org/10.1007/s00704-023-04363-x.
Guo
B.
,
Chen
Z.
,
Guo
J.
,
Liu
F.
,
Chen
C.
&
Liu
K.
2016
Analysis of the nonlinear trends and non-stationary oscillations of regional precipitation in Xinjiang, Northwestern China, using ensemble empirical mode decomposition
.
International Journal of Environmental Research & Public Health
13
(
3
),
345
.
https://doi.org/10.3390/ijerph13030345
.
Hu
Y.
,
Zhou
B.
,
Han
T.
,
Li
H.
&
Wang
H.
2022
In-phase variations of spring and summer droughts over Northeast China and their relationship with the North Atlantic Oscillation
.
Journal of Climate
35
(
21
),
6923
6937
.
https://doi.org/10.1175/JCLI-D-22-0052.1
.
Huang
N. E.
&
Wu
Z.
2008
A review on Hilbert-Huang transform: Method and its applications to geophysical studies
.
Reviews of Geophysics
46
(
2
),
RG2007
.
https://doi.org/10.1029/2007RG000228
.
Huang
N. E.
,
Shen
Z.
,
Long
S.
,
Wu
M. C.
,
Shih
H.
,
Zheng
Q.
,
Yen
N.
,
Tung
C.
&
Liu
H.
1998
The empirical mode decomposition and the Hilbert spectrum for nonlinear and non-stationary time series analysis
.
Proceedings: Mathematical, Physical and Engineering Sciences
454
(
1971
),
903
995
.
doi:10.1098/rspa.1998.0193
.
Li
F.
,
Zhang
G.
&
Xu
Y.
2014a
Spatiotemporal variability of climate and streamflow in the Songhua River Basin, northeast China
.
Journal of Hydrology
514
,
53
64
.
https://doi.org/10.1016/j.jhydrol.2014.04.010.
Li
W.
,
Fu
X.
,
Wu
W.
&
Wu
B.
2014b
Study on runoff and sediment process variation in the lower Yellow River
.
Journal of Hydroelectric Engineering
33
(
1
),
108
113
.
https://doi.org/CNKI:SUN:SFXB.0.2014-01-017
.
Li
B.
,
Chen
Z.
&
Yuan
X.
2015
The nonlinear variation of drought and its relation to atmospheric circulation in Shandong Province, East China
.
PeerJ
3
(
22
),
e1289
.
https://doi.org/10.7717/peerj.1289.
Li
T.
,
Zhou
Z.
,
Fu
Q.
,
Liu
D.
,
Mo
L.
,
Hou
R.
,
Wei
P.
&
Li
L.
2020
Analysis of precipitation changes and its possible reasons in Songhua River Basin of China
.
Journal of Water and Climate Change
11
(
3
),
839
864
.
https://doi.org/10.2166/wcc.2019.250
.
Liu
W.
,
Zhu
S.
,
Huang
Y.
,
Wan
Y.
,
Wu
B.
&
Liu
L.
2020
Spatiotemporal variations of drought and their teleconnections with large-scale climate indices over the Poyang Lake Basin, China
.
Sustainability
12
(
9
),
3526
.
https://doi.org/10.3390/su12093526
.
Luo
X.
,
Luo
X.
,
Ji
X.
,
Ming
W.
,
Wang
L.
,
Xiao
X.
,
Xu
J.
,
Liu
Y.
&
Li
Y.
2023
Meteorological and hydrological droughts in the Lancang-Mekong River Basin: Spatiotemporal patterns and propagation
.
Atmospheric Research
293
,
106913
.
https://doi.org/10.1016/j.atmosres.2023.106913.
Manzano
A.
,
Clemente
M. A.
,
Morata
A.
,
Yolanda Luna
M.
,
Begueria
S.
,
Vicente-Serrano
S. M.
&
Luisa Martin
M.
2019
Analysis of the atmospheric circulation pattern effects over SPEI drought index in Spain
.
Atmospheric Research
230
,
104630
.
https://doi.org/10.1016/j.atmosres.2019.104630
.
Mckee
T. B.
,
Doesken
N. J.
&
Kleist
J.
1993
The relationship of drought frequency and duration to time scales
. In
Proceedings of the 8th Conference on Applied Climatology
.
American Meteorological Society
,
Boston
,
1993
, pp.
179
184
.
Mohammad
K.
,
Mansour
A.
,
Salam
M. A.
,
Mondol
A. H.
,
Rahman
A.
,
Deb
L.
,
Kundu
K. P.
,
Zaman
A. U.
&
Islam
A. R.
2022
Spatiotemporal drought analysis in Bangladesh using the standardized precipitation index (SPI) and standardized precipitation evapotranspiration index (SPEI)
.
Scientific Reports
12
(
1
),
20694
.
https://doi.org/10.1038/s41598-022-24146-0.
Palmer
W. C.
1965
Meteorological drought. U.S. Department of Commerce Weather Bureau Research Paper
.
Rahman
M. R.
&
Lateh
H.
2016
Meteorological drought in Bangladesh: Assessing, analysing and hazard mapping using SPI, GIS and monthly rainfall data
.
Environmental Earth Sciences
75
(
12
),
1026
.
https://doi.org/10.1007/s12665-016-5829-5
.
Shen
G.
,
Zheng
H.
&
Lei
Z.
2017
Applicability analysis of SPEI for drought research in Northeast China
.
Acta Ecologica Sinica
37
(
11
),
3787
3795
.
https://doi.org/10.5846/stxb201604160706
.
Singh
A.
,
Thakur
S.
&
Adhikary
N. C.
2020
Influence of climatic indices (AMO, PDO, and ENSO) and temperature on rainfall in the Northeast Region of India
.
SN Applied Sciences
2
(
10
),
1728
.
https://doi.org/10.1007/s42452-020-03527-y
.
Song
X.
,
Song
S.
,
Sun
W.
,
Mu
X.
,
Wang
S.
,
Li
J.
&
Li
Y.
2015
Recent changes in extreme precipitation and drought over the Songhua River Basin, China, during 1960–2013
.
Atmospheric Research
157
(
15
),
137
152
.
https://doi.org/10.1016/j.atmosres.2015.01.022
.
Song
X.
,
Yu
S.
&
Chen
Y.
2020
Secular trend of global drought since 1950
.
Environmental Research Letters
15
(
9
),
094073
.
https://doi.org/10.1088/1748-9326/aba20d.
Suroso
N. D.
,
Ardiansyah
&
Edvin
A.
2021
Drought detection in Java Island based on standardized precipitation and evapotranspiration index (SPEI)
.
Journal of Water and Climate Change
12
(
6
),
2734
2752
.
https://doi.org/10.2166/wcc.2021.022
.
Tong
S.
,
Bao
Y.
,
Te
R.
,
Ma
Q.
,
Ha
S.
&
Lusi
A.
2017
Analysis of drought characteristics in Xilingol Grassland of Northern China based on SPEI and its impact on vegetation
.
Mathematical Problems in Engineering
2017
(
3
),
1
11
.
https://doi.org/10.1155/2017/5209173
.
Vicente-Serrano
S. M.
,
Beguería
S.
&
López-Moreno
J. I.
2009
A multi-scalar drought index sensitive to global warming: The standardized precipitation evapotranspiration index – SPEI
.
Journal of Climate
23
(
7
),
1696
1718
.
https://doi.org/10.1175/2009JCLI2909.1
.
Wang
F.
,
Wang
Z.
,
Yang
H.
,
Di
D.
&
Zhao
Y.
2018
Study of the temporal and spatial patterns of drought in the Yellow River basin based on SPEI
.
Science China(Earth Sciences)
61
(
08
),
1098
1111
.
https://doi.org/10.1007/s11430-017-9198-2
.
Wang
F.
,
Wang
Z.
,
Yang
H.
,
Di
D.
,
Zhao
Y.
&
Liang
Q.
2020
Utilizing GRACE-based groundwater drought index for drought characterization and teleconnection factors analysis in the North China Plain
.
Journal of Hydrology
585
,
124849
.
https://doi.org/10.1016/j.jhydrol.2020.124849.
Wang
L.
,
Zhang
J.
,
Elmahdi
A.
,
Shu
Z.
,
Wu
Y.
&
Wang
G.
2022
Evolution characteristics and relationship of meteorological and hydrological droughts from 1961 to 2018 in Hanjiang River Basin, China
.
Journal of Water and Climate Change
13
(
1
),
224
246
.
doi:10.2166/wcc.2021.267
.
Wondimu
T. H.
,
Tenalem
A.
&
Sirak
T.
2023
A comparative study of drought characteristics using meteorological drought indices over the central main Ethiopian Rift
.
Hydrology Research
54
(
3
),
313
329
.
https;//doi.org/10.2166/nh.2023.091
.
Wu
Z.
&
Huang
N. E.
2004
A study of the characteristics of white noise using the empirical mode decomposition method
.
Proceedings Mathematical Physical & Engineering Sciences
460
(
2046
),
1597
1611
.
https://doi.org/10.1098/rspa.2003.1221.
Wu
Z. H.
&
Huang
N. E.
2011
Ensemble empirical mode decomposition: A noise assisted data analysis method
.
Advances in Adaptive Data Analysis
1
(
01
),
1
41
.
https://doi.org/10.1142/S1793536909000047.
Wu
Y. F.
&
Zhang
G.
2018
Spatio-temporal patterns of meteorological and hydrological drought in the Songhua river area from 1961 to 2010
.
Scientia Geographica Sinica
38
(
10
),
1731
1739
.
https://doi.org/10.13249/j.cnki.sgs.2018.10.018
.
Wu
W.
,
Ji
F.
,
Hu
S.
&
He
Y.
2023
Asymmetric drying and wetting trends in Eastern and Western China
.
Advances in Atmospheric Sciences
12
(
4
),
933
.
https://doi.org/10.1007/s00376-022-2216-x.
Yang
P.
,
Zhai
X.
,
Huang
H.
,
Zhang
Y.
,
Zhu
Y.
,
Shi
X.
,
Zhou
L.
&
Fu
C.
2023
Association and driving factors of meteorological drought and agricultural drought in Ningxia, Northwest China
.
Atmospheric Research
289
,
106753
.
https://doi.org/10.1016/j.atmosres.2023.106753
.
Ye
L.
,
Shi
K.
,
Zhang
H.
,
Xin
Z.
,
Hu
J.
&
Zhang
C.
2019
Spatio-temporal analysis of drought indicated by SPEI over northeastern China
.
Water
11
(
5
),
908
.
https://doi.org/10.3390/w11050908
.
Yu
S.
,
Zhang
X.
,
Liu
Z.
,
Wang
Y.
&
Shen
Y.
2023
Spatial and temporal variations of extreme climate index in the Songhua River Basin during 1961–2020
.
Chinese Journal of Applied Ecology
34
(
4
),
1091
1101
.
https://doi.org/10.13287/j.1001-9332.202304.024.
Zeng
D.
,
Yuan
X.
&
Roundy
J. K.
2019
Effect of teleconnected land-atmosphere coupling on Northeast China persistent drought in Spring-Summer of 2017
.
Journal of Climate
32
(
21
),
7403
7420
.
https://doi.org/10.1175/JCLI-D-19-0175.1
.
Zhang
X.
,
Zhao
Y.
&
Guo
L.
2019
Aquatic ecological functional zoning of Songhua River Basin based on data fusion technology
.
Journal of Harbin Institute of Technology
51
(
8
),
80
87
.
https://doi.org/10.11918/j.issn.0367-6234.201804119.
Zhao
R.
,
Sun
H.
,
Xing
L.
,
Li
R.
&
Li
M.
2023
Effects of anthropogenic climate change on the drought characteristics in China: From frequency, duration, intensity, and affected area
.
Journal of Hydrology
617
,
129008
.
https://doi.org/10.1016/j.jhydrol.2022.129008.
This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY-NC-ND 4.0), which permits copying and redistribution for non-commercial purposes with no derivatives, provided the original work is properly cited (http://creativecommons.org/licenses/by-nc-nd/4.0/).

Supplementary data