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Article

Characteristics of Potential Evapotranspiration Changes and Its Climatic Causes in Heilongjiang Province from 1960 to 2019

1
School of Water Conservancy and Electric Power, Heilongjiang University, Harbin 150006, China
2
School of Water Conservancy and Civil Engineering, Northeast Agricultural University, Harbin 150030, China
3
Key Laboratory of Efficient Use of Agricultural Water Resources, Ministry of Agriculture and Rural Affairs of the People’s Republic of China, Northeast Agricultural University, Harbin 150030, China
4
College of Agriculture, Northeast Agricultural University, Harbin 150030, China
5
Department of Science and Technology, Heilongjiang University, Harbin 150006, China
6
College of Agricultural Science and Engineering, Hohai University, Nanjing 210024, China
7
College of Civil Engineering and Water Conservancy, Heilongjiang Bayi Agricultural University, Daqing 163319, China
8
Xingyang Water Conservancy Bureau, Zhengzhou 450000, China
*
Author to whom correspondence should be addressed.
Agriculture 2022, 12(12), 2017; https://doi.org/10.3390/agriculture12122017
Submission received: 17 October 2022 / Revised: 21 November 2022 / Accepted: 24 November 2022 / Published: 26 November 2022
(This article belongs to the Special Issue Modeling the Adaptations of Agricultural Production to Climate Change)

Abstract

:
Climate change refers to the statistically significant changes in the mean and dispersion values of meteorological factors. Characterizing potential evapotranspiration (ET0) and its climatic causes will contribute to the estimation of the atmospheric water cycle under climate change. In this study, based on daily meteorological data from 26 meteorological stations in Heilongjiang Province from 1960 to 2019, ET0 was calculated by the Penman–Monteith formula, linear regression method and the Mann–Kendall trend test were used to reveal the seasonal and inter-annual changing trend of ET0. The sensitivity-contribution rate method was used to clarify the climatic factors affecting ET0. The results showed that: (1) From 1960 to 2019, the maximum temperature (Tmax), minimum temperature (Tmin) and average temperature (Tmean) showed an increasing trend, with climate tendency rate of 0.22 °C per decade (10a), 0.49 °C/(10a), 0.36 °C/(10a), respectively. The relative humidity (RH), wind speed (U) and net radiation (Rn) showed a decreasing trend, with a climate tendency rate of −0.42%/(10a), −0.18 m/s/(10a), −0.08 MJ/m2/(10a), respectively. (2) ET0 showed a decreasing trend on seasonal and inter-annual scales. Inter-annually, the average climate tendency rate of ET0 was −8.69 mm/(10a). seasonally, the lowest climate tendency rate was −6.33 mm/(10a) in spring. (3) ET0 was negatively sensitive to Tmin, and RH, while positively sensitive to Tmax, Tmean U and Rn, its sensitivity coefficient of U was the highest, which was 1.22. (4) The contribution rate of U to ET0 was the highest on an inter-annual scale as well as in spring and autumn, which were −8.96%, −9.79% and −13.14%, respectively, and the highest contribution rate to ET0 were Rn and Tmin in summer and winter, whose contribution rates were −4.37% and −11.46%, respectively. This study provides an understanding on the response of evapotranspiration to climatic change and further provides support on the optimal allocation of regional water resource and agricultural water management under climate change.

1. Introduction

Over the past 100 years (1906–2005), the global average surface temperature has increased by 0.74 °C and is expected to increase by at least 4 °C in 2100 if carbon dioxide emissions are not reduced [1]. Climate change will inevitably lead to changes in the global hydrological cycle [2]. Apart from precipitation and runoff, actual evapotranspiration (ET) is the most important climatic factor and a main component in the hydrological cycle [3]. Evapotranspiration is affected by a variety of meteorological factors, such as temperature, relative humidity (RH), wind speed (U), and net radiation (Rn). Characteristics of ET changes and its climatic causes under climate change will reveal the water cycle process and its driving mechanism.
Due to the complexity of the ET process, it is difficult to directly measure the ET: however, with the deepening of vegetation ET research, obtaining regional continuous ET data by calculating the ET becomes particularly vital. Potential evapotranspiration (ET0), as the basis for calculating the ET [4], represents the maximum ET that can be achieved on a fixed underlying surface with unlimited water supply under certain meteorological conditions. ET0 is widely used in the analysis of climate dry and wet conditions, rational use and evaluation of water resources, crop water demand and agricultural production management, and ecological environment research [5]. There are many ways to calculate ET0, such as temperature and the solar radiation-based Hargreaves method, the equilibrium evaporation-based Priestley-Taylor model and the FAO Blaney–Criddle formula [6]. However, many scholars choose the Penman-Monteith method recommended by the FAO56 to calculate ET0. The advantage of the Penman–Monteith method is that standard meteorological data are easily obtained or obtained through routine observation, and all calculation procedures can be standardized by the calculation of available meteorological data and time scales [7].
ET0 was heterogeneous in temporal and spatial distribution. Jung et al. [8] pointed out that the global average annual ET increased at a rate of 7.1 ± 1.0 mm/10a from 1982 to 1997, but since 1998, the global average ET decreased by −7.9 mm/10a. Roderick et al. [9] found that in the past 50 years, the ET0 in the northern hemisphere was decreasing at a faster rate of 2 to 4 mm/a. ET0 also showed an increasing trend in some areas, such as West Africa [10] and Turkey [11]. Wu et al. [12] pointed out that the national annual average ET0 decreased at a rate of 0.52 mm/a based on the daily meteorological data of 552 meteorological stations in China from 1961 to 2015, and the ET0 of most stations in arid and humid regions showed a significant decreasing trend; however, neither the increasing nor decreasing trend of ET0 is significant in semi-arid and semi-humid regions. The decrease or increase of ET0 may affect the hydrological cycle differently. For example, when the ET0 decreases, the transport of water vapor in the atmosphere is reduced, resulting in corresponding changes in precipitation patterns. For agriculture, the water use efficiency of crops may be improved by reducing the adverse effects of drought on crops. However, the increase of ET0 will increase water consumption, resulting in increased land water loss and drought, and the atmospheric circulation may be affected, which may lead to strong rainfall, thus changing the distribution of water resources.
The spatio–temporal heterogeneity of ET0 was attributed to the common effect of different climatic factors, including maximum temperature (Tmax), minimum temperature (Tmin), average temperature (Tmean), RH, U and sunshine hours, while the dominant factors affecting ET0 varied in different regions. For example, Bandyopadhyay et al. [13] concluded that the main reason for the decrease of ET0 in India was the significant increase in RH and decrease of U by the non-parametric method of Sen’s slope. Roderick et al. [14] believed that the decrease in solar radiation caused by the increase in cloud cover and aerosol concentration in the southern hemisphere was the main reason for the decrease of ET0 in New Zealand. Hossein et al. [15] believed that U has the greatest impact on ET0 in Iranian region under arid climate condition by sensitivity analysis. Guo et al. [16] used the Sobol global sensitivity analysis method to analyze the sensitivity of ET0 in Australia calculated by the Penman–Monteith and Priestley–Taylor models and obtained that air temperature was the most sensitive factor to ET0. China has seven geographic regions, with complex and diverse climatic characteristics. ET0 has shown a fluctuating downward trend in recent decades, such as Henan Province in Central China [17], Anhui Province in East China [18], Sichuan Basin [19] and Huaihe basin [20] in Southwest China; the results of the sensitivity-contribution rate method showed that the contribution of U to ET0 was higher than that of sunshine hours, indicating that U was the dominant meteorological factor in the above area. On the contrary, in North China, the results of the sensitivity coefficient method showed that sunshine hours were the dominant factor, followed by U [21]. Zhou et al. [22] analyzed the partial correlation between ET0 and meteorological factors by discussing climate attribution and concluded that the increase of the Tmax in the Three River Headwaters region located in Northwest China was the main reason for the increasing trend of ET0, however, the contribution of U was the smallest among all meteorological factors, which was different from the meteorological factors affecting the trend of ET0 in other regions.
Heilongjiang Province, located in one of the four major black soil belts in the world, has an existing land area of 454,600 km2 and an area of 23,900 km2 of arable land. It is the largest province in terms of grain production in the country. In recent years, Heilongjiang Province has become one of the regions with the largest temperature rise in the country and one of the regions with more serious climate disasters, threatening the safe production of food crops. The impact of floods and droughts on the agricultural economy in Heilongjiang Province accounted for about 89.4% of the total impact of various natural disasters [23]; the reduction of grain production due to floods and droughts accounted for about 12% of the total grain output in the same period [24]. Nie et al. [25] speculated that the climate in Heilongjiang Province would continue to warm in the next 30 and 50 years, and water resources would be scarcer. The probability of drought is increasing. ET0, as a key factor to characterize the regional dry and wet conditions, is of great significance for guiding water resource management and agricultural production management in Heilongjiang Province. Jiang et al. [26] expounded on the various characteristics of ET0 in Heilongjiang Province from the scale of the crop growing season and pointed out that ET0 was the most sensitive to RH, which provided an important reference index for formulating a reasonable irrigation system for the crop growing season in Heilongjiang Province. However, their study was limited to the growing season of crops, which could not fully reflect the changes of ET0 in Heilongjiang Province between inter-annual and different seasons; moreover, contributing rates of different climate factors were not analyzed. Su et al. [27] pointed out that the contribution rate of water vapor pressure and U to the ET0 change in Heilongjiang Province was the largest by multiple regression analysis, and it has a certain significance for understanding the influencing factors on the inter-annual change of ET0. However, they failed to study the impact of more meteorological factors on a shorter time scale. The weather of Heilongjiang Province changes significantly in four seasons, and ET0 may be affected by different climatic factors in seasonal scales.
This study used a linear regression equation and the Mann–Kendall method to analyze the trend of ET0 in Heilongjiang Province in the past 60 years on the inter-annual and seasonal scales. The sensitivity coefficient and contribution of different climate factors to ET0 were comprehensively analyzed by the sensitivity-contribution rate method, aiming to provide an important basis for the rational and efficient use of water resources and agricultural water management in different regions of Heilongjiang Province under climate change.

2. Materials and Methods

2.1. Overview of the Study Area and Data Sources

Heilongjiang Province, located in the east of Eurasia, is the northernmost province with the highest latitude in China, starting at 121°11′ in the west, 135°05′ in the east, 43°26′ in the south, and 53°33′ in the north, spanning 14 longitudes from east to west and 10 latitudes from north to south, with an average altitude of 481 m. It has a temperate continental monsoon climate. It spans the four major river systems of the Heilongjiang River, Wusuli River, Songhua River and Suifenhe River. The average annual temperature of Heilongjiang Province is between −5 and 5 °C, gradually increasing from the north to the south. The annual precipitation is between 400 and 650 mm, with more in the central mountainous areas, followed by the east, and less in the west and north. The annual sunshine hours in the province are mostly between 2400 and 2800 h, where the west is more than the east.
The meteorological data in this study were from the daily meteorological data of 26 meteorological stations (Figure 1) in Heilongjiang Province from 1960 to 2019 recorded by the China Meteorological Data Network, including Tmax, Tmin, Tmean, RH, U, and sunshine hours; Rn was calculated according to the method recommended by the Food and Agriculture Organization of the United Nations (FAO) [7]. According to the meteorological division method, March to May is divided into spring, June to August is summer, September to November is autumn, and December to February is winter [28].

2.2. Mann–Kendall Trend and Mutation Test

For the time series X, (containing n samples), an order column is constructed:
S k = i = 1 k r i   ( k = 2 ,   3 ,   ,   n )
where
r i = {   + 1     x i > x j 0           o r   ( j = 1 ,   2 , ,   i )
The order column Sk is the sum of the number of values when the value of the i moment is greater than the j moment.
Under the assumption that the time series is random, define the statistic:
U F k = [ S k E ( S k ) ] V a r ( S k )   ( k = 1 ,   2 , ,   n )
where UF1 = 0, E(Sk) and Var(Sk) are the mean and variance of Sk, respectively, and when X1, X2,…, Xn are independent of one other, they have the same continuous distribution, which can be deduced from the following equation:
E ( S k ) = n ( n + 1 ) 4 ,   V a r ( S k ) = n ( n 1 ) ( 2 n + 5 ) 72 ( 2 k n )
UFk is a standard normal distribution, it is a sequence of statistics calculated in the order of time series X (X1, X2,…, Xn); given the significance level α by checking the normal distribution table, if UFi > Uα, it indicates that there is a significant trend change in the sequence. Then repeat the above process in the reverse order of time series X (Xn, Xn−1,…, X1) and make UBk = UFk (k = n, n−1, …, 1), UB1 =0.
Generally, if the significance level α = 0.05, then the critical value Z = ±1.96. The curves of the two statistical sequences of UF, UB and the two straight lines of ±1.96 are plotted on one plot. If the values of UF and UB are greater than 0, it indicates an upward trend in the series, and if the values of UF and UB are less than 0, it indicates a downtrend. When UF and UB exceed the critical line, it indicates a significant upward or downward trend, and the range above the critical line is determined as the time zone in which the mutation occurred. If the two curves of UF and UB intersect and the intersection point is between the critical lines, then the moment corresponding to the intersection point is the time when the mutation begins [29].

2.3. Climate Tendency Rate

The climate tendency rate was calculated by the least squares method, and the unary linear regression equation of Yi and Xi was established:
Yi = AXi + B
where A and B are regression constants, and A × 10 is the climate tendency rate, representing the changing rate of each climatic factor every 10 years (10a). A positive value indicates an increasing trend of climate in the corresponding time series, while a negative value indicates a decreasing trend.

2.4. Calculation of ET0

The daily ET0 of 26 sites in Heilongjiang Province was calculated using the Penman–Monteith model recommended by the FAO. The formula is as follows:
E T 0 = 0.408 Δ ( R n G ) + γ 900 T + 273 U 2 ( e s e a ) Δ + γ ( 1 + 0.34 U 2 )
where ET0 is the potential evapotranspiration, mm; Δ is the slope of the temperature change with the saturated water vapor pressure, kPa/°C; Rn is the surface net radiation, MJ/(m2·d); G is the soil heat flux, MJ/(m2·d); γ is the hygrometer constant, kPa/°C; U2 is the U at a height of 2 m above the ground, m/s; es is the saturated vapor pressure, kPa; ea is the actual vapor pressure, kPa; T is the temperature, °C.

2.5. Sensitivity-Contribution Rate Method Based on Partial Derivatives

Sensitivity analysis makes each input variable change within the corresponding value range, and studies and predicts the influence degree of the changes of these input variables on the output value. The influence degree is called the sensitivity coefficient [30] and is used to judge the interference degree of the relative changes of climatic factors to the changes of ET0. This paper mainly analyzed the sensitivity and contribution rate of Tmax, Tmin, Tmean, RH, U and Rn to ET0. The sensitivity coefficient Svi of ET0 to each climatic factor was calculated by the following formula:
S v i = lim Δ 0 ( Δ E T 0 Δ v i · E T 0 v i ) = E T 0 v i · v i E T 0
where vi is the climatic factor; Svi is the sensitivity coefficient of the climatic factor. The positive and negative values of Svi reflect the correlation between ET0 and climatic factor. A negative sensitivity coefficient indicates that ET0 decreases with the decrease of climatic factors, and vice versa. The absolute value reflects the impact of climatic factors on ET0. The greater the absolute value, the greater the impact, and vice versa.
The contribution rate Gvi is equal to Svi multiplied by the annual change rate of meteorological variables (Rvi), which is:
R v i = n × T r e n d v i | a v v i | × 100 %
G v i = R v i · S v i
where Rvi is the annual relative change rate of vi; n is the total number of years; Trendvi is the annual climate tendency rate of vi, which is the slope of the univariate linear regression equation between vi and n; avvi is the annual average value of vi; Gvi is the contribution rate, the magnitude of the absolute value of Gvi reflects the contribution of the relative change of vi to the change of ET0.

2.6. Data Processing

The CROPWAT 8.0 (FAO, Rome, Italy) software was used to calculate the daily ET0 by the Penman–Monteith formula, Matlab 2021a (MathWorks, Natick, MA, USA) was used to calculate the rate of change of ET0, Tmax, Tmin, Tmean, RH, U and Rn, and perform a Mann–Kendall mutation test. The Mann–Kendall test was used to analyze the long-term change trend and mutation of ET0. The ArcMap 10.4 (ESRI, Redlands, CA, USA) toolkit was used for spatial analysis to perform spatial interpolation and mapping for each meteorological variable, the spatial interpolation method was Inverse Distance Weighting (IDW) and the spatial resolution was 500 dpi.

3. Results

3.1. Spatial Distribution of the Mean Values of Meteorological Factors

Spatial distribution of average Tmax, Tmin, Tmean, RH, U, Rn from 1960 to 2019 is shown in Figure 2. On the inter-annual scale, the Tmax, Tmin and Tmean showed an increasing trend from north to south, their inter-annual ranges were 5.5~11.5 °C, 0.5~7.0 °C and 1.0~5.5 °C, respectively. A higher RH was mainly distributed in the central region, while the RH in east and west region was relatively lower. A higher U was mainly distributed in the east and west regions. Spatially, Rn increased from north to south.
On the seasonal scale, the Tmax, Tmin and Tmean also showed an increasing trend from north to south. The RH was higher in summer and lower in spring. However, the U was higher in spring and lower in summer, which were 3.71 m/s and 2.67 m/s, respectively. The Rn is larger in summer and smaller in winter; the ranges were 11.5~12.8 MJ/m2 and 0.30~1.90 MJ/m2, respectively.

3.2. Temporal and Spatial Variation of the Climate Tendency Rate of Meteorological Factors

At time series on inter-annual and seasonal scales, the Tmax, Tmin, Tmean showed a significant upward trend (p < 0.05) for Tmax in winter (Table 1). Whereas, the RH, U and Rn showed a significant downward trend (p < 0.05), except for RH in spring and summer, U in autumn and Rn in autumn and winter. The inter-annual climate tendency rate for the Tmax, Tmin, Tmean, RH, U and Rn was 0.22 °C/10a, 0.49 °C/10a, 0.36 °C/10a, −0.42 (%/10a), −0.18 (m/s/10a), and −0.04 (MJ/m2/10a), respectively.
In terms of spatial distribution on inter-annual scales, the Tmax, Tmin, and Tmean showed an increasing trend, higher climate tendency rate of them were mainly distributed in the northern region (Figure 3). The RH showed a decreasing climate tendency rate except for some central and southern regions. The U was shown a decreasing trend except Jixi, and the climate tendency rate was lower in western and higher in central region. The Rn showed a decreasing climate tendency rate except for Hulin and Tonghe. On seasonal scales, The Tmax, Tmin, and Tmean showed an increasing trend except for Tmax in Suifenhe and Tmean in Hulin in summer. The climate tendency rate of Tmax, Tmin, Tmean were greatest in winter compared with the other 3 seasons (Figure 3). The RH showed a decreasing climate tendency rate except in the central regions in spring, summer, and autumn. The climate tendency rate of U was lower in the western and eastern regions, and the climate tendency rate of Rn showed a decreasing trend except for some central and eastern regions.

3.3. Temporal and Spatial Variation of ET0

ET0 was the highest in summer and lowest in winter, with daily averages of 4.11 mm and 0.35 mm, respectively (Figure 4). ET0 showed decreasing trends in seasons and inter-annual; the higher ET0 values were mainly distributed in the southwest region. The average climate tendency rate of ET0 in spring, summer, autumn, winter and inter-annual was −6.33 mm/(10a), −2.72 mm/(10a), −2.58 mm/(10a), −0.65 mm/(10a), and −8.69 mm/(10a), respectively (Figure 4). In the western region, the seasonal lower ET0 climate tendency rate, especially in spring and summer, led to a more rapid decrease trend of inter-annual ET0.
The inter-annual ET0 in Heilongjiang Province showed a significant increasing trend from 1977 to 1983 (Z > 1.96), while it showed a significant decreasing trend in 2017–2019 (Z < −1.96). The mutation point of ET0 appeared in 2011, and the changing trend of ET0 changed from increase to decrease (Figure 5e). On a seasonal scale, the mutation years range from 2006 to 2015 (Figure 5a–d).

3.4. Sensitivity of ET0 to Meteorological Factors

The sensitivity coefficients of ET0 to U, Rn, RH, Tmax, Tmin and Tmean are shown in Table 2. On the inter-annual scale, in the case that other climatic factors remain unchanged, when the U, Rn, Tmax, Tmean, RH and Tmin increase by 10%, ET0 will increase by 12.2%, 4.0%, 4.2%, 1.4% or decrease by 11.5% and 1.4%, respectively. The sensitivity order of ET0 change to each climatic factor was U > RH > Tmax > Rn > Tmin = Tmean.
On the seasonal scale (Table 2), the changes of ET0 in spring, summer and autumn were all negatively sensitive to RH, positively sensitive to U, Rn, Tmax, and Tmean, while the changes of ET0 to RH, Tmax, Tmin and Tmean were negatively sensitive in winter. ET0 was most sensitive to U in spring and autumn, and most sensitive to RH and Tmin in summer and winter, with sensitivity coefficients of 1.35, 1.40, −0.91 and −1.76, respectively.
Figure 6 shows the spatial distribution of sensitivity coefficients of ET0. On the inter-annual scale, The sensitivity coefficients of ET0 to Tmax, Tmin and Tmean gradually increased from north to south. The sensitivity coefficients of ET0 to RH decreased from west to east. A higher sensitivity coefficient to U was mainly distributed in the eastern and western regions, while the sensitivity coefficient to Rn was mainly distributed in the central region.
On the seasonal scales, the sensitivity of ET0 to Tmax, Tmin, Tmean was higher in the western region in spring and summer, and higher in the southeast and south in autumn and winter. ET0 showed lower sensitivity to RH in the central region throughout the 4 seasons, the sensitivity coefficient of ET0 to U was higher in spring and autumn, while the sensitivity coefficient of ET0 to Rn was higher in summer.

3.5. Dominant Climatic Factors for ET0 Change

On the inter-annual scale, U was the dominant climatic factor for the change of ET0, followed by Tmax, Tmean, RH, Rn and Tmin, with contribution rates of 6.15%, 5.03%, 4.34%, −1.82%, and −1.41%, respectively (Table 3). The positive contribution rates of RH, Tmax and Tmean to ET0 have not been able to offset the negative contribution rates of U, Rn and Tmin; therefore, the ET0 showed a decreasing trend from 1960 to 2019.
On the seasonal scale, U was the dominant factor for the decrease of ET0 in spring and autumn, followed by Tmax and RH; the largest contribution rates to the change of ET0 were −9.79% and −13.14%, respectively. In summer, Rn was the dominant factor for ET0 change, the contribution rates of Tmax, Tmin, and Tmean to ET0 were less different, which were 2.57%, 2.1% and 2.09%,respectively, while in winter, Rn contributes the least to ET0, and Tmin became the dominant factor.
The spatial distribution of dominant meteorological factors is shown in Figure 7. In spring, the dominant factor for ET0 was U in the study area except for Fujin (Figure 7a), In summer, Rn was the dominant factor in most regions of the study area, Tmin and RH were the dominant factors in the partial northern and eastern regions. In autumn, U was the dominant factor for 85% of the total 26 sites (Figure 7c); in winter, Tmin was the dominant factor in the northern and eastern regions, while U was the dominant factor in the western region. On the inter-annual scale, the dominant factor of all 26 sites was U (Figure 7e).

4. Discussion

Under the general warming of the global climate, ET0 was on the rise in most areas, such as the annual ET0 for India, which, as a whole, has increased in the latter half of the 20th century [31]; Awash River basin, Ethiopia [32], and South Korea over the recent 100 years [33], which is consistent with the generally accepted trend that ET0 increases with temperature. However, the phenomenon of the “evaporation paradox” appeared in many areas around the world [34], that is, with the continuous increase of temperature, the ET0 showed a decreasing trend, such as the Canadian prairie region, the northern region of South America, Thailand, New Zealand [9,35,36,37], and the northwest of India [38], the Lijiang watershed [39], as well as Alor Setar, Malaysia [40]. In this study, ET0 in Heilongjiang Province from 1960 to 2019 showed a decrease trend inter-annually and seasonally with the increasing temperature, proving that the “evaporation paradox” phenomenon also existed in our study area, which was consistent with the conclusion of Li et al. [41]. At present, there is still no clear conclusion about the mechanism of the “evaporation paradox”; the existing related research studies are mostly qualitative analysis, and the reasons need to be further explored.
In China, the sensitivity coefficient and contribution rate of ET0 to meteorological factors varied in different climatic regions. Even in the same climatic region, the sensitivity coefficient and contribution rate of ET0 were different spatially. For example, in the subtropical monsoon climate zone, ET0 in the Yangtze River basin [42], Sichuan basin [43], and Yunnan-Guizhou plateau [44] were most sensitive to the Tmax, RH, and sunshine hours, respectively. In the temperate continental climate zone, ET0 in the middle and upper reaches of the Yellow River [45] and the Ebinur Lake basin in Xinjiang [46] were most sensitive to the actual water vapor pressure and U, respectively, with the highest contribution rate of U for both regions. In the plateau mountainous climate region, the meteorological factor with the largest sensitivity coefficient in the Qinghai Tibet Plateau was the actual water vapor pressure, and the sunshine hours had the largest contribution rate to ET0 [47]. Our study area is located in the temperate monsoon climate zone, where ET0 was the most sensitive to U and had the largest contribution rate to ET0. However, in the Loess Plateau basin, which is also located in the same climate zone, ET0 was most sensitive to actual water vapor pressure and Tmean had the highest contribution rate [48]. In the North China Plain of the temperate monsoon climate zone, sunshine hours had the largest contribution rate to ET0 [21]. In summary, the plateau area has strong solar radiation, long sunshine time, and low temperature, which may cause the ET0 to be most affected by the sunshine hours; most of the basin areas have a dry climate, less rainfall, and lack of water resources, causing vegetation to be more sensitive to the water condition; therefore, RH might have a larger sensitivity coefficient to ET0. Heilongjiang Province is located in plain and mountainous areas, and affected by southeast monsoon in summer and controlled by northwest monsoon in winter [49]. This might be the reason why U contributed the most to ET0 change.
In this study, ET0 in Heilongjiang Province showed a decrease trend on the inter-annual scale from 1960 to 2019, with U as the dominant factor, which was consistent with the trend of ET0 in Jilin Province analyzed by Liu et al. [50] and in Liaoning Province analyzed by Cao et al. [51]. This was probably because the above three provinces are geographically contiguous and have a similar type of climate characteristics. A research established by Xu et al. in 2003 predicted that the temperature in Heilongjiang Province would increase significantly by 2030 and 2050 with a higher increase in winter and a lower increase in summer by the CCCma (Canadian Center for Climate Modelling and analysis), CCSR (Center for Climate System Research), CSIRO (Commonwealth Scientific and Industrial Research Organization), GFDL (Geophysical Fluid Dynamics Laboratory) and Hadley climate models [52]. Zhang et al. [53] pointed out that the climate of Heilongjiang Province would tend to be warm and humid in the next 41 years by the Hadley model. Wang et al. [54] believed that ET0 was not only affected by various meteorological factors, but interactions between meteorological factors would also interfere with ET0 changes. Moreover, ET0 may also be affected by human activities including aerosol emissions, air pollution [55] and rice area expansion [56]. Therefore, further exploration in these aspects will be needed for contribution analysis of ET0 changes in Heilongjiang Province in the future, as well as in other regions of the world.

5. Conclusions

In this study, ET0 was calculated by the Penman–Monteith formula, the sensitivity-contribution rate method was used to clarify the climatic factors affecting seasonal and inter-annual changing of ET0., The Tmax, Tmin, Tmean showed an increasing trend and RH, U, Rn showed a decreasing trend from 1960 to 2019. ET0 showed a decreasing trend with an average climate tendency rate of −8.69 mm/(10a). The annual average ET0 change was negatively sensitive to Tmin and RH, and positively sensitive to Tmax, Tmean, U and Rn. U was the dominant factor for the ET0 decrease in spring and autumn, while RH and Tmin were the dominant factors in summer and winter, respectively. On the inter-annual scale, the sensitivity order of ET0 change to each climatic factor was U > RH > Tmax > Rn > Tmin = Tmean. These results indicated that the dominant factors for ET0 changes were U in Heilongjiang Province. Moreover, the dominant factors for ET0 change varies under different climatic and geographical conditions; impacts of human activities on ET0 should also be considered in future studies.

Author Contributions

Conceptualization, T.N.; methodology, T.N. and R.Y.; software, R.Y.; validation, R.Y., S.L. X.Z. and Y.L.; formal analysis, T.N. and R.Y.; data curation, P.C. and T.L.; writing—original draft preparation, T.N. and R.Y.; writing—review and editing, Z.G., C.D. (Chong Du), C.D. (Changlei Dai) and H.J.; visualization, R.Y.; supervision, T.N., Z.Z. and Z.G.; funding acquisition, T.N. and Z.Z. All authors have read and agreed to the published version of the manuscript.

Funding

This work was fund by the Opening Project of Key Laboratory of Efficient Use of Agricultural Water Resources, Ministry of Agriculture and Rural Affairs of the People’s Republic of China (number: AWR2021002), the Basic Scientific Research Fund of Heilongjiang Provincial Universities (number: 2021-KYYWF-0019), the National Key Research and Development Program of China (2021YFD1500802) and the National Natural Science Foundation Project of China (numbers: 51779046 & 52079028).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We thank the anonymous reviewers and the editors for their suggestions which substantially improved the manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. IPCC. Climate Change 2007: The Physical Science Basis; Cambridge University Press: Cambridge, UK, 2007. [Google Scholar]
  2. Silva, C. Importance of modelling and its feasibility in the future climate in Sri Lanke. Symp. Water Prof. Day 2013, 18, 15–28. [Google Scholar]
  3. Anabalón, A.; Sharma, A. On the divergence of potential and actual evapotranspiration trends: An assessment across alternate global datasets. Earth’s Future 2017, 9, 905–917. [Google Scholar] [CrossRef]
  4. Ding, Y.H. Introduction to Climate Change Science in China; China Meteorological Press: Beijing, China, 2008; Volume 128. [Google Scholar]
  5. Abedi-Koupai, J.; Dorafshan, M.M.; Javadi, A. Estimating potential reference evapotranspiration using time series models (case study: Synoptic station of Tabriz in northwesternIran). Appl. Water Sci. 2022, 12, 212. [Google Scholar] [CrossRef]
  6. Li, Y.L.; Cui, J.Y.; Zhang, T.H. A comparative study on the calculation methods of reference crop evapotranspiration. China Desert 2002, 04, 65–69. [Google Scholar]
  7. Pereira, L.S.; Allen, R.G.; Smith, M. Crop evapotranspiration estimation with FAO56: Past and future. Agric. Water Manag. 2015, 147, 4–20. [Google Scholar] [CrossRef]
  8. Jung, M.; Reichstein, M.; Ciais, P.; Seneviratne, S.I.; Goulden, M.L.; Bonan, G.; Cescatti, A.; Chen, J.Q.; De, J. Recent decline in the global land evapotranspiration trend due to limited moisture supply. Nature 2010, 467, 951–954. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  9. Roderick, M.L.; Farquhar, G.D. Changes in New Zealand pan evaporation since the 1970s. Int. J. Climatol. 2005, 25, 2031–2039. [Google Scholar] [CrossRef]
  10. Onyutha, C. Statistical analyses of potential evapotranspiration changes over the period 1930–2012 in the Nile River riparian countries. Agric. For. Meteorol. 2016, 226–227, 80–95. [Google Scholar] [CrossRef]
  11. Dadaser-Celik, F.; Cengiz, E.; Guzel, O. Trends in reference evapotranspiration in Turkey: 1975–2006. Int. J. Climatol. 2016, 36, 1733–1743. [Google Scholar] [CrossRef] [Green Version]
  12. Wu, X.; Wang, P.J.; Huo, Z.G.; Bai, Y.M. Spatio-temporal distribution characteristics of potential evapotranspiration and impact factors in China from 1961 to 2015. Resour. Sci. 2017, 39, 964–977. [Google Scholar]
  13. Bandyopadhyay, A.; Bhadra, A.; Raghuwanshi, N.S.; Singh, R. Temporal trends in estimates of reference evapotranspiration over India. J. Hydrol. Eng. 2014, 14, 508–515. [Google Scholar] [CrossRef]
  14. Roderick, M.L.; Farquhar, G.D. Changes in Australian pan evaporation from 1970 to 2002. Int. J. Climatol. 2004, 24, 1077–1090. [Google Scholar] [CrossRef]
  15. Tabari, H.; Talaee, P.H. Sensitivity of evapotranspiration to climatic change in different climates. Glob. Planet. Chang. 2014, 115, 16–23. [Google Scholar] [CrossRef]
  16. Guo, D.L.; Westra, S.; Holger, R.M. Sensitivity of potential evapotranspiration to changes in climate variables for different Australian climatic zones. Hydro. Earth Syst. Sci. 2017, 21, 2107–2126. [Google Scholar] [CrossRef] [Green Version]
  17. Zhang, Z.G.; Zheng, M.J.; Cai, M.T.; Yin, J.Y.; Li, H.H.; Wang, Y.W. Spatio-temporal evolution and genesis analysis of reference crop evapotr-anspiration in Henan Province from 1960 to 2019. Water Sav. Irrig. 2021, 3, 44–50. (In Chinese) [Google Scholar]
  18. Wu, W.Y.; Kong, Q.Q.; Wang, X.D.; Ma, X.Q.; He, B.F.; Zhang, H.Q. Sensitivity analysis of reference crop evapotranspiration in Anhui Province in the past 40 years. J. Ecol. Environ. 2013, 22, 1160–1166. [Google Scholar]
  19. Zhao, L.; Liang, C. Study on the causes of changes in potential evapotranspiration in Sichuan Province in the past 50 years. Soil Water Conserv. Res. 2014, 21, 26–30. (In Chinese) [Google Scholar]
  20. Wang, X.D.; Ma, X.Q.; Xu, Y.; Lui, R.N.; Cao, W.; Zhu, H. The variation characteristics of reference crop evapotranspiration and the contribution of main meteorological factors in the Huaihe River Basin. China Agric. Meteorol. 2013, 34, 661–667. (In Chinese) [Google Scholar]
  21. Wang, P.T.; Yan, J.P.; Jiang, C.; Liu, X.F. Spatial-temporal variation of reference crop evapotranspiration and its influencing factors in North China Plain. Acta Ecol. Sin. 2014, 34, 5589–5599. [Google Scholar]
  22. Zhou, B.R.; Li, F.X.; Xiao, H.B.; Hu, A.J.; Yan, L.D. Temporal and spatial differentiation characteristics of potential evapotranspiration and climate attribution in the source region of the Three Rivers. J. Nat. Resour. 2014, 29, 2068–2077. [Google Scholar]
  23. Wang, Q.J.; Lv, J.J.; Li, X.F.; Wang, P.; Ma, G.Z. Distribution characteristics of agricultural meteorological disasters in Heilongjiang Province and their impact on agricultural production. Heilongjiang Water Conserv. Sci. Technol. 2016, 44, 57–61. (In Chinese) [Google Scholar]
  24. Zhang, P. Analysis on the Causes of Agricultural Natural Disasters in Heilongjiang Province. Res. Agric. Mech. 2011, 33, 249–252. [Google Scholar]
  25. Nie, T.Z.; Tang, Y.; Jiao, Y.; Li, N.; Wang, T.Y.; Du, C.; Zhang, Z.X.; Chen, P.; Li, T.C.; Sun, Z.Y.; et al. Effects of Irrigation Schedules on Maize Yield and Water Use Efficiency under Future Climate Scenarios in Heilongjiang Province Based on the AquaCrop Model. Agronomy 2022, 12, 810. [Google Scholar] [CrossRef]
  26. Jiang, Y.; Du, C.; Sun, H.N.; Zhong, Y. Spatio-temporal variation characteristics and sensitivity analysis of potential evapotranspiration during crop growing season in Heilongjiang Province under climate change. Hydropower Energy Sci. 2018, 36, 6–9. (In Chinese) [Google Scholar]
  27. Su, J.W.; Zhang, X.L.; Shen, B. Spatio-temporal variation characteristics and influencing factors of potential evapotranspiration in Heilongjiang. Heilongjiang Water Conserv. Sci. Technol. 2021, 49, 1–8. (In Chinese) [Google Scholar]
  28. Tu, A.G.; Li, Y.; Nie, X.F.; Mo, M.H. Changes of reference crop evapotranspiration in Poyang Lake Basin and its attribution analysis. Ecol. Environ. Sci. 2017, 26, 211–218. [Google Scholar]
  29. Xing, L.T.; Huang, L.X.; Chi, G.Y.; Yang, L.Z.; Li, C.S.; Hou, X.Y. A Dynamic Study of a Karst Spring Based on Wavelet Analysis and the Mann-Kendall Trend Test. Water 2018, 10, 698. [Google Scholar] [CrossRef] [Green Version]
  30. Xing, H.H.; Chen, H.D.; Lin, H.Y. Sensitivity analysis of hierarchical hybrid fuzzy-neural network based on input perturbation. Software 2013, 34, 52–55. [Google Scholar]
  31. Sarma, A.; Bhaskar, V.V.; Sastry, C.M. Potential Evapotranspiration over India—An estimate of Green Water flow. Mausam 2014, 65, 365–378. [Google Scholar] [CrossRef]
  32. Yadeta, D.; Kebede, A.; Tessema, N. Potential evapotranspiration models evaluation, modelling, and projection under climate scenarios, Kesem sub-basin, Awash River basin, Ethiopia. Model. Earth Syst. Environ. 2020, 6, 2165–2176. [Google Scholar] [CrossRef]
  33. Jeon, M.G.; Nam, W.H.; Mun, Y.S.; Yoon, D.H.; Yang, M.H.; Lee, H.J.; Shin, J.H.; Hong, E.M.; Zhang, X. Climate change impacts on reference evapotranspiration in South Korea over the recent 100 years. Theor. Appl. Climatol. 2022, 150, 309–326. [Google Scholar] [CrossRef]
  34. Roderick, M.L.; Farquhar, G.D. The cause of decreased pan evaporation over the past 50 years. Science 2002, 298, 1410–1411. [Google Scholar] [CrossRef] [PubMed]
  35. Burn, D.H.; Hesch, N.M. Trends in evaporation for the Canadian Prairies. J. Hydrol. 2007, 336, 61–73. [Google Scholar] [CrossRef]
  36. Quintana-Gomez, R.A. Changes in evaporation patterns detected in northernmost South America: Homogeneity testing. In Proceedings of the 7th International Meeting on Statistical Climatology, Whisler, BC, Canada, 25–29 May 1998. [Google Scholar]
  37. Tebakari, T.C.; Yoshitani, J.C.; Suvanpimol, C.C. Time-space trend analysis in pan evaporation over Kingdom of Thailand. J. Hydrol. Eng. 2005, 10, 205–215. [Google Scholar] [CrossRef]
  38. Das, P.K.; Midya, S.K.; Das, D.K.; Rao, G.S.; Raj, U. Characterizing Indian meteorological moisture anomaly condition using long-term (1901–2013) gridded data: A multivariate moisture anomaly index approach. Int. J. Climatol. 2018, 38, E144–E159. [Google Scholar] [CrossRef]
  39. Jiao, L.; Wang, D.M. Climate Change, the Evaporation Paradox, and Their Effects on Streamflow in Lijiang Watershed. Pol. J. Environ. Stud. 2018, 27, 2585–2591. [Google Scholar] [CrossRef]
  40. Ahmad, A.A.; Yusof, F.; Mispan, M.R.; Kamaruddin, H. Rainfall, evapotranspiration and rainfall deficit trend in Alor Setar, Malaysia. Malays. J. Fundam. Appl. Sci. 2017, 13, 400–404. [Google Scholar] [CrossRef]
  41. Li, X.F.; Jiang, L.X.; Li, X.F.; Zhao, F.; Zhu, H.X.; Wang, P.; Gong, L.J.; Zhao, H.Y. Evolution characteristics of evaporation and its relationship with climatic factors in Heilongjiang Province from 1961 to 2017. Meteorology 2021, 47, 755–766. (In Chinese) [Google Scholar]
  42. Liu, C.M.; Zhang, D.; Liu, X.M.; Zhao, C.S. Spatial and temporal change in the potential evapotranspiration sensitivity to meteorological factors in China (1960–2007). J. Geogr. Sci. 2012, 22, 3–14. (In Chinese) [Google Scholar] [CrossRef]
  43. Chen, D.D.; Wang, X.D.; Wang, S.; Su, X.W. Variation of potential evapotranspiration and its climatic influencing factors in Sichuan Province. Chin. J. Agrometeorol. 2017, 38, 548–557. (In Chinese) [Google Scholar]
  44. Yu, F.; Gu, X.P.; Xiong, H. Spatio-temporal variation characteristics of potential evapotranspiration in Guizhou and sensitivity to meteorological factors. Agric. Sci. Technol. 2015, 16, 2845–2848. (In Chinese) [Google Scholar]
  45. Wang, Y.J.; Li, J.; Lin, Z.H.; Tong, X.J.; Xing, X.M. Estimation of the potential evapotranspiration effects of climate change on the middle and upper reaches of the Yellow River. Chin. J. Soil Water Conserv. 2013, 11, 48–56. (In Chinese) [Google Scholar]
  46. Xu, J.J.; Jin, X.Y.; Qiang, H.F.; Dai, H.; Liang, C. Characteristics and causes of potential evapotranspiration change in The Ebi Lake Basin in Xinjiang. J. Irrig. Drain. 2018, 37, 89–94. [Google Scholar]
  47. Shi, Y. Climate Change on the Tibetan Plateau and Its Impact on Potential Evapotran-Spiration; Beijing Forestry University: Beijing, China, 2019. [Google Scholar]
  48. Ning, T.T. Spatial-Temporal Variation of Evapotranspiration in the Loess Plateau under Budyko Framework and Its Attribution Analysis; Research Center for Soil and Water Conservation and Eco-Environment of the Ministry of Education; Chinese Academy of Sciences: Beijing, China, 2017. (In Chinese) [Google Scholar]
  49. Chen, P.; Xu, J.; Zhang, Z.; Wang, K.; Li, T.; Wei, Q.; Li, Y. Carbon pathways in aggregates and density fractions in Mollisols under water and straw management: Evidence from 13C natural abundance. Soil. Biol. Biochem. 2022, 169, 108684. [Google Scholar] [CrossRef]
  50. Liu, Y.X.; Ren, J.Q.; Wang, D.N.; Mu, J.; Cui, J.L.; Chen, C.S.; Chen, X.; Guo, C.M. Spatio-temporal distribution and genesis analysis of reference crop evapotranspiration in Jilin Province. J. Ecol. Environ. 2019, 28, 2208–2215. [Google Scholar]
  51. Cao, Y.Q.; Qi, J.W.; Wang, F.; Li, L.H.; Lu, J. Evolution law and attribution analysis of potential evapotranspiration in Liaoning Province. Acta Ecol. Sin. 2020, 40, 3519–3525. [Google Scholar]
  52. Xu, N.P.; Pan, H.S.; Xu, Y.; Zhang, G.H. Climate change prediction of Heilongjiang Province in the next 30 and 50 years. J. Nat. Disasters 2004, 1, 146–150. [Google Scholar]
  53. Zhang, J.T.; Feng, L.P.; Pan, Z.H. Climate change trend and mutation analysis in Heilongjiang Province in the next 41 years. Meteorol. Environ. 2014, 37, 60–66. [Google Scholar]
  54. Wang, Q.; Zhang, M.J.; Pan, S.K.; Ma, X.N.; Li, F.; Liu, W.L. Spatial-temporal variation characteristics of potential evapotranspiration in the Yangtze River Basin. Chin. J. Ecol. 2013, 32, 1292–1302. (In Chinese) [Google Scholar]
  55. Ning, T.; Li, Z.; Liu, W.; Han, X. Evolution of potential evapotranspiration in the northern Loess Plateau of China: Recent trends and climatic drivers. Int. J. Climatol. 2016, 36, 4019–4028. [Google Scholar] [CrossRef]
  56. Hu, X.; Chen, M.; Liu, D.; Li, D.; Jin, L.; Liu, S.; Cui, Y.; Dong, B.; Khan, S.; Luo, Y. Reference evapotranspiration change in Heilongjiang Province, China from 1951 to 2018: The role of climate change and rice area expansion. Agric. Water Manag. 2021, 253, 106912. [Google Scholar] [CrossRef]
Figure 1. Map of the study area and distribution of meteorological stations in Heilongjiang Province.
Figure 1. Map of the study area and distribution of meteorological stations in Heilongjiang Province.
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Figure 2. Spatial distribution of average (Row A) Tmax, (Row B) Tmin, (Row C) Tmean, (Row D) RH, (Row E) U, (Row F) Rn from 1960 to 2019.
Figure 2. Spatial distribution of average (Row A) Tmax, (Row B) Tmin, (Row C) Tmean, (Row D) RH, (Row E) U, (Row F) Rn from 1960 to 2019.
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Figure 3. Climatic tendency rate of (Row A) Tmax, (Row B) Tmin, (Row C) Tmean, (Row D) RH, (Row E) U, (Row F) Rn from 1960 to 2019.
Figure 3. Climatic tendency rate of (Row A) Tmax, (Row B) Tmin, (Row C) Tmean, (Row D) RH, (Row E) U, (Row F) Rn from 1960 to 2019.
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Figure 4. (Row A) spatial distribution and (Row B) climate tendency of ET0 from 1960 to 2019.
Figure 4. (Row A) spatial distribution and (Row B) climate tendency of ET0 from 1960 to 2019.
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Figure 5. Mann–Kendall (MK) analysis of ET0 in (a) spring, (b) summer, (c) autumn, (d) winter and (e) inter-annually from 1960 to 2019.
Figure 5. Mann–Kendall (MK) analysis of ET0 in (a) spring, (b) summer, (c) autumn, (d) winter and (e) inter-annually from 1960 to 2019.
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Figure 6. Spatial distribution of sensitivity coefficients of ET0 to (Row A) Tmax, (Row B) Tmin, (Row C) Tmean, (Row D) RH, (Row E) U, (Row F) Rn from 1960 to 2019.
Figure 6. Spatial distribution of sensitivity coefficients of ET0 to (Row A) Tmax, (Row B) Tmin, (Row C) Tmean, (Row D) RH, (Row E) U, (Row F) Rn from 1960 to 2019.
Agriculture 12 02017 g006aAgriculture 12 02017 g006b
Figure 7. Spatial distribution of dominant climatic factors in (a) spring, (b) summer, (c) autumn, (d) winter and (e) inter-annually in the study area from 1960 to 2019.
Figure 7. Spatial distribution of dominant climatic factors in (a) spring, (b) summer, (c) autumn, (d) winter and (e) inter-annually in the study area from 1960 to 2019.
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Table 1. Seasonal and inter-annual climate tendency rate of meteorological factors in Heilongjiang Province.
Table 1. Seasonal and inter-annual climate tendency rate of meteorological factors in Heilongjiang Province.
Climatic FactorsSpringSummerAutumnWinterInter-Annual
Tmax (°C/(10a))0.25 *0.16 *0.19 *0.280.22 *
Tmin (°C/(10a))0.57 *0.39 *0.43 *0.65 *0.49 *
Tmean (°C/(10a))0.41 *0.26 *0.31 *0.47 *0.36 *
RH (%/(10a))−0.13−0.28−0.51 *−0.78 *−0.42 *
U (m/s/(10a))−0.24 *−0.14 *−0.18−0.15 *−0.18 *
Rn (MJ/m2/(10a))−0.05 *−0.10 *−0.01−0.01−0.04 *
Note: * indicates a significant level of 0.05.
Table 2. Sensitivity coefficients of seasonal and inter-annual ET0 change to climate factors.
Table 2. Sensitivity coefficients of seasonal and inter-annual ET0 change to climate factors.
SeasonURnRHTmaxTminTmean
Spring1.350.36−0.120.44−0.100.25
Summer0.400.65−0.910.690.410.55
Autumn1.400.28−1.340.39−0.140.15
Winter0.530.10−1.67−1.64−1.76−1.32
Inter-annual1.220.40−1.150.42−0.140.14
Table 3. Contribution of seasonal and inter-annual climate factors to ET0 changes from 1960 to 2019.
Table 3. Contribution of seasonal and inter-annual climate factors to ET0 changes from 1960 to 2019.
Time ScalesContribution Rates/%Total Contribution/%Dominant Factor
URnRHTmaxTminTmean
Spring−9.79−1.560.186.04−5.823.14−7.81U
Summer−3.63−4.372.022.572.12.090.78Rn
Autumn−13.14−0.37.334.7−4.53.78−2.13U
Winter−10.86−0.33.09−10.1−11.46−9.33−38.96Tmin
Inter-annual−8.96−2.823.345.15−1.414.03−0.67U
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Nie, T.; Yuan, R.; Liao, S.; Zhang, Z.; Gong, Z.; Zhao, X.; Chen, P.; Li, T.; Lin, Y.; Du, C.; et al. Characteristics of Potential Evapotranspiration Changes and Its Climatic Causes in Heilongjiang Province from 1960 to 2019. Agriculture 2022, 12, 2017. https://doi.org/10.3390/agriculture12122017

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Nie T, Yuan R, Liao S, Zhang Z, Gong Z, Zhao X, Chen P, Li T, Lin Y, Du C, et al. Characteristics of Potential Evapotranspiration Changes and Its Climatic Causes in Heilongjiang Province from 1960 to 2019. Agriculture. 2022; 12(12):2017. https://doi.org/10.3390/agriculture12122017

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Nie, Tangzhe, Rong Yuan, Sihan Liao, Zhongxue Zhang, Zhenping Gong, Xi Zhao, Peng Chen, Tiecheng Li, Yanyu Lin, Chong Du, and et al. 2022. "Characteristics of Potential Evapotranspiration Changes and Its Climatic Causes in Heilongjiang Province from 1960 to 2019" Agriculture 12, no. 12: 2017. https://doi.org/10.3390/agriculture12122017

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