Journal Pre-proofs Research papers A global quantitation of factors affecting evapotranspiration variability Feng Shuyun, Jianyu Liu, Qiang Zhang, Yongqiang Zhang, Vijay P. Singh, Xihui Gu, Peng Sun PII: DOI: Reference:
S0022-1694(20)30148-7 https://doi.org/10.1016/j.jhydrol.2020.124688 HYDROL 124688
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Journal of Hydrology
Received Date: Revised Date: Accepted Date:
30 June 2019 24 January 2020 12 February 2020
Please cite this article as: Shuyun, F., Liu, J., Zhang, Q., Zhang, Y., Singh, V.P., Gu, X., Sun, P., A global quantitation of factors affecting evapotranspiration variability, Journal of Hydrology (2020), doi: https://doi.org/10.1016/ j.jhydrol.2020.124688
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1
A global quantitation of factors affecting evapotranspiration
2
variability Feng Shuyun1, Jianyu Liu1, Qiang Zhang2,3,4, Yongqiang Zhang5, Vijay P. Singh6, Xihui
3
Gu7, Peng Sun8
4 5 6
1Laboratory
of Critical Zone Evolution, School of Geography and Information Engineering,
7
China University of Geosciences, Wuhan 430074, China
8
2Key
9
Beijing Normal University, Beijing 100875, China
Laboratory of Environmental Change and Natural Disaster, Ministry of Education,
10
3State
Key Laboratory of Earth Surface Processes and Resource Ecology, Beijing Normal
11
University, Beijing 100875, China
12
4Faculty
13
Management, Beijing Normal University, Beijing 100875, China
14
5CSIRO
15
6Department
16
Engineering, Texas A&M University, College Station, Texas, USA
17
7Department
18
Geosciences, Wuhan 430074, China;
19
8College
20
Corresponding author: Qiang Zhang (
[email protected]); Jianyu Liu (
[email protected])
of Geographical Science, Academy of Disaster Reduction and Emergency
Land and Water, GPO Box 1700, Canberra ACT 2601, Australia of Biological and Agricultural Engineering and Zachry Department of Civil
of Atmospheric Science, School of Environmental Studies, China University of
of Geography and Tourism, Anhui Normal University, Anhui 241000, China
21
1
22
Abstract: Scientific viewpoints on the long-term hydrological responses to factors
23
other than climatic change remain controversial and yet the impacts of these factors are
24
often neglected at the short-term (such as monthly and annual) timescale. We developed
25
an analytical method to decompose evapotranspiration (E) variability to the variability
26
of precipitation (P), potential evapotranspiration (E0), total water storage change (∆S),
27
and catchment characteristics (n), such as vegetation, soil and climate seasonality.
28
Global assessment showed that P enhanced E variability in most regions, while
29
restrained E variability in some extremely humid regions. E0 controlled monthly E
30
variability in most the energy-constrained regions. ∆S had much larger impacts on E
31
variability at monthly scale compared to the annual scale, and restrained E variability
32
in many arid regions (P/E0 < 0.66). Catchment characteristics had larger impacts on E
33
variability in humid regions (P/E0 > 0.66), especially at annual scale. The dominant
34
factors of E variability varied with timescales and regions. At a global scale, P and
35
catchment characteristics are the dominant factors controlling global E variability at
36
monthly and annual scales, respectively; In humid regions, however, the impacts of E0
37
on monthly E variability are generally larger than the impacts of precipitation and
38
catchment characteristics. We highlight the necessity to consider the impacts of
39
catchment characteristics even at the short-term timescales, otherwise the simulation
40
and attribution of E variability would be significantly underestimated.
41
Keywords: Climate change; Global evapotranspiration; Attribution; Budyko
42
framework; Different timescales
43 2
44
1
Introduction
45
Quantitatively attributing the causes of global hydrometeorological change is
46
important to understanding the global hydrological cycle and energy balance, and
47
supports hydrological modeling, prediction, and management (Berghuijs et al., 2017;
48
Berghuijs and Woods, 2016a; Haddeland et al., 2014; Liu et al., 2017a; Yang et al.,
49
2017; Zhou et al., 2015). Recent global studies indicated that catchment characteristics
50
(as summarized by n or ω in Budyko framework, also named as “other factors”), such
51
as vegetation, soil and climate seasonality, have important impacts on water cycle at
52
long-term timescale (Berghuijs et al., 2017; Berghuijs and Woods, 2016a; Berghuijs
53
and Woods, 2016b; Chen et al., 2016; Gudmundsson et al., 2016; Gudmundsson et al.,
54
2017; Zhou et al., 2015).
55
Zhou et al. (2015) found that catchment characteristics had a larger impact on water
56
yield (runoff/precipitation, R/P) in more humid regions, and their contribution tended
57
to
58
evapotranspiration, P/E0). On the contrary, Gudmundsson et al. (2017) advocated that
59
catchment characteristics influenced water yield in more arid conditions and their
60
contribution decreased with the increase of wetness index. These discrepancies
61
demonstrated limited understanding of the roles of catchment characteristics in water
62
availability and variability under different dry-wet conditions, and their conflicting
63
results may cause divergence in both scientific conclusions and water management.
64
Therefore, revisiting the factors affecting hydrometeorological changes globally and
65
clarifying of the impacts of catchment characteristics are necessary for a better
increase
with
the
increase
of
wetness
3
index
(precipitation/potential
66
understanding of hydrometeorological processes under the changing environment.
67
The variability of E, which is directly related to water yield, reflects the sensitivity
68
of hydroclimatic responses to the changes of climatic variables and catchment
69
characteristics (Zeng and Cai, 2016; Zhang et al., 2016a). Recent years have witnessed
70
increasing efforts in the quantification of causes behind the E variability in different
71
regions and basins. Koster and Suarez (1999) were the first to derive the standard
72
deviation of E at annual scale based on the Budyko framework. Some studies extended
73
the Budyko hypothesis to a finer time scale for hydrological sensitivity and variability
74
analysis by considering total water storage change (ΔS) (Liu et al., 2018; Wang and
75
Alimohammadi, 2012; Ye et al., 2015; Zeng and Cai, 2015). Integrating the effect of
76
ΔS, Zeng and Cai (2015) developed a theoretical framework to assess the sources of E
77
variability from variance and covariance of P, E0 and ΔS:
78 79
𝜎2𝐸 = 𝑤2𝑃𝜎2𝑃 + 𝑤2𝐸0𝜎2𝐸0 + 𝑤2𝑇𝑊𝑆𝐶𝜎2𝑇𝑊𝑆𝐶 + 𝑤𝑃,𝐸0𝑐𝑜𝑣(𝑃,𝐸0) +𝑐𝑜𝑣(𝑃,𝑇𝑊𝑆𝐶) + 𝑤𝐸0,𝑇𝑊𝑆𝐶 ∙ 𝑐𝑜𝑣(𝐸0,𝑇𝑊𝑆𝐶)
(1)
80
This equation is meaningful to extend the hydrological attribution from long-term
81
timescale to short-term timescales, such as monthly and annual scales. Based on this
82
equation, Zeng and Cai (2016) evaluated the influencing factors behind monthly and
83
annual E variability across 32 large rivers over the globe. Also, some studies applied
84
this framework in attribution analysis of E and runoff (R) variability across China (Wu
85
et al., 2017; Zhang et al., 2016a). However, some issues need to be addressed in the
86
derivation and application of this equation in attribution analysis: (1) This method
87
attributes the variance of E to the variance and covariance of P, E0 and ΔS, e.g., 𝜎2𝑃 4
88
and 𝑐𝑜𝑣(𝑃,𝐸0), which makes it impossible to know individual contribution of a single
89
factor. (2) As shown later in this paper, such an approach prohibits accounting for the
90
impacts of catchment characteristics, such as vegetation, soil and climate seasonality,
91
on E variability, which biases the simulation and attribution, and needs to be resolved
92
if we want to a better quantify the attribution of E variability. Previous studies have
93
verified the significant impacts of catchment characteristics on hydrometeorological
94
changes at long-term timescale (Berghuijs et al., 2017; Jaramillo and Destouni, 2014;
95
Lin et al., 2014; Lin et al., 2010; Renner and Bernhofer, 2012), which may also play a
96
role in E variability at short-term timescales, such as monthly and annual scales.
97
However, no reports were found to quantify the impacts of catchment characteristics on
98
monthly and annual E variability, especially at global scale. As suggested by Zhang et
99
al. (2016a), future research is needed to assess the influences of catchment
100
characteristics on the E variability. Therefore, a new analytical method needs to be
101
developed with considering the impacts of catchment characteristics, as well as
102
focusing on the individual contribution of each factor instead of the covariance of two
103
factors.
104
Overall, previous global assessments only attributed the hydrometeorological
105
changes at long-term timescale (Berghuijs et al., 2017; Gudmundsson et al., 2017; Yang
106
and Yang, 2011; Zhou et al., 2015), and there are conflicting findings in the dominant
107
factors of hydrometeorological changes (Gudmundsson et al., 2017; Zhou et al., 2015).
108
Limited attention has been paid to quantitative attribution at short-term timescale (Wu
109
et al., 2017; Zeng and Cai, 2015; Zeng and Cai, 2016; Zhang et al., 2016a), but the 5
110
methods used in these studies only can assess the impacts of climatic factors without
111
considering the impacts of catchment characteristics. Furthermore, no systematic study
112
concerning the sources of monthly and annual E variability across the globe has been
113
published yet. Therefore, the objectives of this study are: (1) to propose a Budyko-based
114
E variability decomposition method with the inclusion of catchment characteristics to
115
assess the sources of E variability; (2) to clarify the impacts of catchment characteristics
116
on E variability under different dry-wet conditions; and (3) to evaluate global patterns
117
of the effects of P, E0, ΔS and catchment characteristics on the variability of E at
118
monthly and annual scales. This study can help shed a new light on
119
hydrometeorological responses to affecting factors over the globe in a changing
120
environment.
121 122
2
Methods and Data
123
2.1 Data
124
Global monthly terrestrial water cycle dataset (Greenland and Antarctica were
125
excluded), including P, E, R and ∆S (1984-2010, 0.5º spatial resolution), were collected
126
from
127
(http://stream.princeton.edu:8080/opendap/MEaSUREs/WC_MULTISOURCES_WB
128
_050) (Zhang et al., 2018). This dataset was merged from multiple data sources, such
129
as in-situ observations, remotely sensed data, land surface model outputs, and
130
reanalysis datasets. For example, the ∆S was merged by simulations from VIC model
131
and ensemble mean of ∆S product derived from GRACE. Compared to most dataset
Terrestrial
Hydrology
Research
6
Group
at
Princeton
University
132
from only one single data source, this dataset was known as the best available global
133
monthly dataset (Wu et al., 2018). Besides, a constrained Kalman filter data
134
assimilation technique was used to obtain the water balance for each month. In addition,
135
this dataset was validated by in-situ observations, such as the observed E data from the
136
FluxNet towers, and the runoff data from the Global Runoff Data Centre (GRDC), and
137
the United States Geological Survey (USGS), which shown that the dataset was reliable
138
and can be used to investigate the impacts of climate variability on hydrological cycle.
139
More details about this dataset, in terms of data sources, data assimilation procedures
140
and uncertainty quantification, can be found in Zhang et al., (2018). The global long-
141
term (1901-2015) monthly E0 dataset was calculated at 0.5° grid resolution by Harris et
142
al. (2014) from Climatic Research Unit (CRU) in the University of East Anglia
143
(https://crudata.uea.ac.uk/cru/data/hrg/), by using the Penman–Monteith equation
144
(Monteith, 1965; Penman, 1948).
145
2.2 Analytical derivation of E variability
146
The Budyko framework shows the water supply and available energy are the
147
controlling factors behind the mean E, which can be presented by a function of P and
148
E0. Based on the Budyko framework, several water-energy balance equations have been
149
deduced, among which the equations by Choudhury (1999) and Yang et al. (2008) have
150
been widely used:
151
𝐸=
𝑃𝐸0
(𝑃
𝑛
+ 𝐸𝑛0)
1/𝑛
(2)
152
where n is the controlling parameter, which can be calibrated by minimizing the least
153
squares errors between the simulated E by equation (2) and assessed E from Global 7
154
monthly terrestrial water cycle dataset. The n accounts for catchment characteristics
155
that impact the partitioning of P on E, such as vegetation, soil and climate seasonality.
156
Limited by steady-state assumption of Budyko framework, the equation (2) was
157
generally used at long-term timescale. Although several studies have applied it to
158
annual timescale, the assumption on ignoring the impacts of Δ S may be not valid.
159
Therefore, by considering the impacts of ΔS, previous studies have extended the
160
Budyko framework to shorter timescale (Wang and Alimohammadi, 2012; Zeng and
161
Cai, 2015):
162
𝐸𝑖 =
(𝑃𝑖 ― ∆𝑆𝑖)𝐸0𝑖
((𝑃𝑖 ― ∆𝑆𝑖)𝑛𝑖 + 𝐸0𝑖𝑛𝑖)
(3)
1/𝑛𝑖
163
where i is the time. If i is the month, this equation is a monthly water-energy balance
164
equation at monthly scale. Then the ni is the mean parameter in the Budyko model for
165
the ith month within one year during all the study periods (Tang et al., 2017; Xing et
166
al., 2018). If i is the year, that is an annual water-energy balance equation at annual
167
scale.
168
Hydrological cycle and water balance are not only controlled by climatic changes,
169
such as P and E0, but also regulated by catchment characteristics (n), such as vegetation,
170
soil and climate seasonality (Fig. 1). Besides, ΔS plays a more important role in the
171
water-energy balance at short-term timescale (Fig. 2), since water storage dynamics is
172
significant at monthly and annual scales (Chen et al., 2013). The E can be expressed as
173
the function of P, E0, ΔS and n, E=f (P, E0, ΔS, n). The total differential of E can be
174
expressed as:
175
𝑑𝐸𝑖 =
∂𝑓
∂𝑃𝑑𝑃𝑖
∂𝑓
∂𝑓
∂𝑓
+ ∂𝐸0𝑑𝐸0𝑖 + ∂∆𝑆𝑑∆𝑆𝑖 + ∂𝑛𝑑𝑛𝑖 8
(4)
176 177
Using a first-order approximation of E change, Eq. (4) can be rewritten as:
178
∆𝐸𝑖 ≈
∂𝑓
∂𝑃∆𝑃𝑖
∂𝑓
∂𝑓
∂𝑓
(5)
+ ∂𝐸0∆𝐸0𝑖 + ∂∆𝑆∆𝑆𝑖 + ∂𝑛∆𝑛𝑖
179
where ∆ represents the departure of a quantity during year/month i from its long-term
180
mean value.
181
To avoid variance and covariance in the analytical derivation, here we evaluate the
182
variability of E by using the mean absolute deviation (MAD), which shows a similar
183
ability to standard deviation (σ) in the evaluation of E variability (Fig. 3).
184
1
1
𝑁
1
𝑁
𝑁
𝑀𝐴𝐷𝐸 = 𝑁∑𝑖 = 1|𝐸𝑖 ― 𝐸| = 𝑁∑𝑖 = 1|∆𝐸𝑖| = 𝑁∑𝑖 = 1𝑠𝑖𝑔𝑛(∆𝐸𝑖) × ∆𝐸𝑖
(6)
185 186
where N is the sample size. Substituting ∆𝐸𝑖 from Eq. (4) into Eq. (5), we can develop
187
an analytical derivation for E variability:
188
1
𝑁
𝑀𝐴𝐷𝐸 = 𝑁∑𝑖 = 1𝑠𝑖𝑔𝑛(∆𝐸𝑖) ×
(
∂𝑓
∂𝑃𝑑𝑃𝑖
∂𝑓
∂𝑓
∂𝑓
)
+ ∂𝐸0𝑑𝐸0𝑖 + ∂∆𝑆𝑑∆𝑆𝑖 + ∂𝑛𝑑𝑛𝑖
(7)
189
The E variability predicated by Eq. (7) is referred to “simulation”; while the E
190
variability assessed by standard deviation with the E data from Zhang et al. (2018) is
191
referred to “assessment”. Eq. (7) can be presented as:
192
𝑀𝐴𝐷𝐸 = 𝐼𝑃 + 𝐼𝐸0 + 𝐼∆𝑆 + 𝐼𝑛
(8)
193
where 𝐼𝑃, 𝐼𝐸0, 𝐼∆𝑆 and 𝐼𝑛 indicate the impacts of P, 𝐸0, ∆𝑆 and catchment
194
characteristics on the E variability, respectively: 1
∂𝑓
𝑁
195
𝐼𝑥 = 𝑁∑𝑖 = 1𝑠𝑖𝑔𝑛(∆𝐸𝑖) × ∂𝑥𝑑𝑥𝑖
196
where x denotes each factor, including P, E0, ∆S, and n.
9
(9)
The absolute contribution of each influencing factor to the E variability (Cx) can be
197 198
quantified as (Hobbins, 2016):
199
𝐶𝑥 = |𝐼
𝑃|
𝐼𝑥 + |𝐼𝐸0| + |𝐼∆𝑆| + |𝐼𝑛|
× 100%
(10)
200
The E variability is subject to temporal shifts at different time scales, such as daily,
201
monthly, annual, and long-term time scales (Zeng and Cai, 2015). Ideally, the analytical
202
derivation of E variability can be applied to assess the sources of E variability at an
203
arbitrary time scale if the E variability can be calculated at that scale. In the current
204
study, we mainly evaluate the influences of P, E0, ∆S and catchment characteristics on
205
the monthly and annual E variability.
206 207
3
Results
208
3.1 Performance of analytical method
209
To verify the reliability of the analytical attribution method, we compared the
210
simulated E variability evaluated by analytical method with the assessed E variability
211
calculated by standard deviation (Fig. 4). Results shown that the analytical method can
212
well capture the E variability at both monthly and annual scales. At the monthly scale,
213
the determination coefficient (R2) and Nash-Sutcliffe coefficient (NSE) between
214
assessed and simulated E variabilities were 0.92 and 0.89, respectively, with a Root
215
Mean Square Error (RMSE) of 2.96 mm (Fig. 4a). If catchment characteristics were not
216
considered in the simulation, the simulated E variability was significantly
217
underestimated with a regression coefficient of 0.78, and the simulation accuracy
218
decreased with R2 and NSE of0.85 and 0.63, respectively (Fig. 4b). 10
219
220
At the annual scale, the R2 and NSE values were 0.90 and0.89, respectively, with a
221
RMSE of 5.16 mm (Fig. 4c). If catchment characteristics were not considered, R2 and
222
NSE reduced to 0.27 and -0.65, and the simulated E variability was also undervalued
223
(Figs. 4d). Furthermore, the simulation accuracy of E variability by the analytical
224
method in arid regions (P/E0 < 0.66) (Feng and Fu, 2013) (R2 ≥ 0.95) was higher than
225
in humid regions (P/E0 > 0.66) (R2 < 0.84) at both monthly and annual scales (Figs. 5),
226
implying larger uncertainty in the E behavior in humid regions than in arid regions.
227
228
The simulation errors also varied with latitude, and there are relatively larger errors
229
around equator. By contrast, the E variability was simulated using the method proposed
230
by Zeng and Cai (2015) , who deduced the variance of E into P, E0 and ΔS without
231
considering the n. Results shows that the E variability simulated by the method from
232
Zeng and Cai (2015) was subject to larger errors than that by the newly-proposed
233
method, and the simulated E variability was underestimated at most latitudes (Figs. 6).
234
This difference mainly because the method developed by Zeng and Cai (2015) ignored
235
the impacts of catchment characteristics.
236 237
3.2. Global patterns of E variability sources
238
Based on Eq. (9-10), we quantified the global pattern of contributions of P, E0, ∆S
239
and catchment characteristics to the E variability. Figures 7 and 8 shows the
240
contributions (measured by percentages) of each factor to E variability, as well as their 11
241
relationships with wetness index (WI; P/E0), at monthly and annual scales, respectively.
242
The positive value means the variability of one factor enhancing the E variability, while
243
the negative value means restraining effect. In general, similar global patterns of
244
contributions at the monthly scale can be observed when compared to that at the annual
245
scale. However, the P and catchment characteristics had larger impacts on the E
246
variability at annual scale, while E0 and ∆S had larger impacts at the monthly scale. In
247
addition, the impacts (including the positive and negative impacts) of P on E variability
248
tend to increase with the WI (wetness index; P/PET), while the impacts of ∆S, E0 and
249
catchment characteristics tend to decrease with the WI.
250
251
P had a positive impact on E variability in most regions across the globe. The
252
contribution of P in arid regions was evidently larger than that in humid regions,
253
epically at annual scale (Figs. 9 and 10), such as West Asia, North Africa, South Africa,
254
Gobi Desert, most regions of Australia, Southwestern America, and Patagonian Desert,
255
with the contribution larger than 50% (Fig. 7 and 8). On the contrary, the contributions
256
of P show negative values in some extreme humid regions, such as Amazon basin,
257
Congo basin, southeast Asia, which implies that more P lead to less E in these regions.
258
Because in these extremely humid regions E is mainly controlled by E0 rather than P.
259
More precipitation is often associated with less solar radiation and larger relative humid
260
(Díaz‐Torres et al., 2017; Solomon, 1967), which reduces the E0 and further leads to
261
the decrease of E (Fig. 11).
262
12
263
∆S had a larger influence on E variability at monthly scale than that at annual scale.
264
The contributions of ∆S are negative in many arid regions. Especially at annual scale,
265
the median contribution of ∆S for arid regions is -2.9%.
266
E0 had much great impacts on E variability in humid regions than that in arid
267
regions, especially at monthly scale, with median contribution of 36.3% for the former
268
while 1.9% for the later.
269
Catchment characteristics enhanced E variability across most regions across the
270
globe, while restrained E variability in some extreme arid regions, such as Sahara Desert,
271
Gobi Desert. Besides, the contributions of n to E variability at annual scale are much
272
larger than that at monthly scale, with median contribution of 41.9% for the former but
273
15.2% for the later.
274
3.3 Identification of key factors behind E variability
275
The key factors behind the E variability were different spatially (Fig. 12).
276
Precipitation is a more important factor behind monthly and annual E variability for 46%
277
and 42% of the global land grid cell, which mainly located in the arid regions.
278
Meanwhile, ∆S had the largest contribution to the E variability across 12% and 2% of
279
the globe at the monthly and annual scales, respectively. In this sense, ∆S had larger
280
impacts on E at shorter time scales, which is agree with the findings in previous study
281
(Wu et al., 2017; Zeng and Cai, 2016; Zhang et al., 2016a). Therefore, Budyko
282
framework should be cautious to use at short-term timescales when the ∆S data is not
283
available.
284
13
285
Regions with a largest contribution of E0 to the annual E variability only accounted
286
for 2%. On the contrary, E0 plays a key role in E variability at monthly scale, and
287
controls the E variability for 32% of global regions. Moreover, in the humid regions,
288
the impacts of E0 on E variability (with median contribution of 36.3%) were generally
289
larger than the impacts of P and catchment characteristics. Catchment characteristics
290
controlled monthly and annual E variability for 10% and 51% of global regions,
291
respectively, implying that catchment characteristics are the dominant factor for global
292
E variability at annual scale.
293
The above-mentioned results indicated that P is the largest contributor to monthly
294
E variability, while catchment characteristics is the largest contributor to annual E
295
variability. ∆S play an important role in E variability at monthly scale. E0 mainly
296
controlled monthly E variability in energy-constrained and moisture-adequate regions.
297
4
Discussion
298
This study has made incremental process on several important aspects of
299
hydrometeorological attributing study. First, a new quantitative framework was
300
developed to attribute E variability at short-term timescales, which has better
301
performance in simulation and attribution of E variability. Second, although several
302
global assessments have investigated the causes of long-term hydrometeorological
303
changes (Berghuijs et al., 2017; Berghuijs and Woods, 2016b; Gudmundsson et al.,
304
2016; Zhou et al., 2015), this study proposed the first quantification attribution of global
305
E variability at short-term timescales, i.e., monthly and annual timescales. Third, the
306
results clarified the roles of catchment characteristics in E variability and challenged 14
307
the widely held view that climate is the primary source of E variability while catchment
308
characteristics are secondary (e.g., Berghuijs et al., 2017; Wu et al., 2017). Our results
309
indicated that the dominant factor of E variability varied with timescales and dry-wet
310
conditions. At a global scale, precipitation played a dominant role in E variability at
311
monthly timescale while catchment characteristics dominated E variability at annual
312
scale; In humid regions, however, the impacts of E0 on monthly E variability are
313
generally larger than the impacts of precipitation and catchment characteristics.
314
Correctly knowledge of the causes of E variability is crucial for understanding of
315
hydrometeorological processes (Wu et al., 2017). Finally, some interesting results were
316
found in the causes of E variability. It is generally recognized that precipitation played
317
a positive role in E variability (Zeng and Cai, 2016; Zhang et al., 2016a). However, the
318
new finding of study is that precipitation restrains E variability in many extremely
319
humid regions, such as Amazon and Congo basins. In contrast, total water storage
320
changes strengthened E variability in most humid regions while restrained E variability
321
in many arid regions.
322
Some previous studies have applied the long-term Budyko equation to annual scale
323
and seems to get reasonable results when neglecting ∆S (Ning et al., 2017; Potter and
324
Zhang, 2009). This is owing to the limited impacts of ∆S on variability at annual
325
timescale (Figure 9b). Nevertheless, the assumption on ignoring ∆S may be not valid
326
(Zeng and Cai, 2016). The regulating effect of ∆S on hydrological response has been
327
well documented (Wang and Alimohammadi, 2012; Zhang et al., 2016a). In the dry
328
months or years, ∆S can provide available water for E and causes larger E than P, which 15
329
enable the Budyko curves poorly capture the E variability (Figure 2a). Due to different
330
roles of ∆S under different arid/humid conditions, ∆S tends to enhance E variability in
331
humid regions but restrains it in the arid regions (Figures 7-8), which is also supported
332
by the findings from Zeng and Cai (2016), Zhang et al. (2016a) and Wu et al. (2017).
333
The ∆S regulated the temporal distribution of water availability for E. In humid regions,
334
∆S hold P from the energy-limited period to a warm period, which increases E in the
335
periods with high energy supply and enhances E variability (Zeng and Cai, 2016). These
336
results imply that, given exclusions of the impacts of ∆S, E variability would be
337
overestimated in arid regions, and underestimated in the humid regions.
338
The P plays a dominant role in E variability in most arid regions. However, in the
339
humid regions, the effect of P on E variability is going to be significantly diminished.
340
By contrast, the E0 has much larger impacts on E variability in humid regions than that
341
in arid regions. These are because the E variability in arid and humid regions are
342
prevalently limited by available water and energy, respectively (Karam and Bras, 2008).
343
The controlling parameter n in Budyko type equation is considered to represent the
344
catchment characteristics, which not only related to vegetation, soil moisture,
345
topography, but also include climate seasonality (Ning et al., 2017), snow rates (Zhang
346
et al., 2015), and storminess (Milly, 1994). Previous studies have found that the values
347
of n have positive relationship with vegetation coverage, soil moisture, while negative
348
relationship with basin slope, climate seasonality, storminess (Li et al., 2013; Liu et al.,
349
2019; Liu et al., 2017b; Padrón et al., 2017; Xu et al., 2013). Based on the Budyko
350
framework, a larger value of n tends to result in a smaller E (Figure 2). Consequently, 16
351
the regions with larger vegetation coverage, higher soil moisture, smaller slope, lower
352
climate seasonality, and less storminess would expect to have a higher n value and a
353
larger E. We emphasized the necessity to consider the impacts of catchment
354
characteristics on the E variability, since previous attributing studies often ignored
355
impacts of catchment characteristics on E changes (Wu et al., 2017; Zeng and Cai, 2016;
356
Zhang et al., 2016a). This argument is not just conceptually important; it play a key role
357
in the attributing results of E variability. For example, Wu et al. (2017) found that E0
358
was the dominant influencing factor behind the annual E variabilty in most regions of
359
South China, which was different from the results shown in Fig. 12. This was because
360
that they only assessed the sources of E variability from climatic factors, but excluded
361
the impacts of catchment characteristics. Our study updated the standing findings
362
concerning the factors behind E (Wu et al., 2017; Zeng and Cai, 2016; Zhang et al.,
363
2016a).
364
Moreover, previous studies showed large errors in the assessment of E variability
365
(Wu et al., 2017; Zeng and Cai, 2016; Zhang et al., 2016a). By attributing monthly E
366
variability to P, E0 and ∆S, Wu et al. (2017) found that the simulated E variability was
367
significantly underestimated, especially in humid regions. Also, the similar cases were
368
obtained in some large river basins over the world (Zeng and Cai, 2016) and lots of
369
small basins across China (Zhang et al., 2016a). Therefore, the remaining question to
370
address is then: why are there obvious underestimation in these studies? Our viewpoint
371
is that previous study ignored the influence of catchment characteristics. The results
372
showed that considering catchment characteristics can greatly improve the simulation 17
373
accuracy of E variability; while if excluding the impacts of catchment characteristics,
374
the E variability could be obvious underestimated and poorly simulated, especially in
375
humid regions. In addition, catchment characteristics had the largest contribution to E
376
changes in humid regions when compared to the impacts of P, E0 and ∆S. Therefore,
377
our study reveals the reason why E variability was often distinctly underestimated in
378
previous attributing study (Wu et al., 2017; Zeng and Cai, 2016), that is because they
379
ignored the contributions of catchment characteristics.
380
Although several studies have investigated the impacts of catchment characteristics
381
globally (Gudmundsson et al., 2016; Zhou et al., 2015), the contribution of catchment
382
characteristics to E is still open for debate (Berghuijs and Woods, 2016b; Chen et al.,
383
2016; Gudmundsson et al., 2017). Zhou et al. (2015) suggested that the contribution of
384
catchment characteristics to E was larger in humid regions than in arid regions, while
385
Gudmundsson et al. (2017) found a larger contribution of catchment characteristics in
386
arid regions, and the same findings were also from Gudmundsson et al. (2016) and
387
Berghuijs et al. (2017). Therefore, no consensus has been reached so far about the
388
impacts of catchment characteristics on E, which can be attributed to different
389
definitions of contributions. Gudmundsson et al. (2017) showed the relative average
390
contribution of finite difference change in m (controlling parameter of Fu’ equation,
391
also referring to the impacts of catchment characteristics) to water yield at the variable
392
range of [P/E0, P/E0 + ∆P/E0] and [m, m + ∆m], while Zhou et al. (2015) suggested the
393
relative contribution of infinitesimal change in m to water yield at exact values of P/E0
394
and m. Moreover, the afore-mentioned studies focused on the water availability changes 18
395
due to a unit change in P/E0 and m, instead of real-world changes. It is noted that a unit
396
change in P/E0 has entirely a different physical interpretation relative to a unit change
397
in m. Therefore, the current assessments are more a theoretical possibility rather than a
398
reality. Hence, taking the monthly and annual variability of E as examples, this study
399
helps shed new light on the real-world impacts of catchment characteristics. Our global
400
patterns of the contributions of P, E0, ∆S and catchment characteristics to the practical
401
E variability showed that catchment characteristics influenced E changes more in humid
402
regions. However, the previous global assessments deemed P or P/E0 as the primary
403
factors (Berghuijs et al., 2017; Gudmundsson et al., 2017; Zhou et al., 2015). For
404
example, Berghuijs et al. (2017) indicated that P controls 83% of the land grid cells for
405
runoff changes and catchment characteristics for the remaining 17%. The difference
406
can be due to different research objects, as well as the difference between practical
407
variability and theoretical changes.
408
The development in our study was based on the Budyko framework. However,
409
there are still some uncertainties and limitations. First, the total differential
410
decomposition of the Budyko formula has inherent errors and uncertainties. Here we
411
did not present uncertainty analysis for the analytical derivation based on the Budyko
412
framework. Yang et al. (2014) estimated the errors of the first-order Taylor expansion
413
of the Budyko-based equation and found that the errors increased with the variability
414
amplitude of the contributor. They showed that a 10 mm increase in precipitation would
415
bring about 0.5-5.0% error in the contribution of precipitation. In addition, we only
416
highlighted the relative contribution of each contributor to the E variability, without 19
417
providing the specific magnitudes of the impacts, since we mainly attempted to
418
investigate the relative importance of these contributors in the E variability.
419
5
Conclusions
420
In this study, we developed an analytical method to assess the sources of E
421
variability. The analytical method simulated the E variability well. We highlighted the
422
necessity to consider the impacts of catchment characteristics although at short-term
423
timescale, since the E variability would be significantly underestimated given exclusion
424
of catchment characteristics.
425
Precipitation played a more important role in E variability in the humid regions and
426
controlled monthly E variability in most regions across the globe. Catchment
427
characteristics were the primary contributor for the annual E variability with median
428
contributions of 51%. E0 had a limited impact on annual E variability, but played a key
429
role in monthly E variability, which controls 32% of global land grid cells. The ∆S had
430
a much large impact at the monthly scale than at the annual scale, which played a
431
dominant role in the monthly E variability for 12% of global land grid cells.
432
In conclusion, the development of analytical derivation for disentangling global E
433
variability has profound implication, which provides a new framework for hydrological
434
attribution analysis at short-term timescales, such as monthly and annual. The results
435
clarifying the role of catchment characteristics and its dominant regions are helpful to
436
improve our understanding on hydrometeorological processes.
437
20
438
Acknowledgments: This work is financially supported by the China National Key
439
R&D Program (Grant 2019YFA0606900), China Postdoctoral Science Foundation
440
funded project (BX20190301), Nature Science Foundation of Hubei Province
441
(2019CFB221), Fundamental Research Funds for the Central Universities, China
442
University of Geosciences (Wuhan) (162301182729), National Science Foundation for
443
Distinguished Young Scholars of China (Grant No. 51425903), the Fund for Creative
444
Research Groups of National Natural Science Foundation of China (Grant No.:
445
41621061), National Natural Science Foundation of China (No. 41771536, No.
446
41401052), Key Project of National Natural Science Foundation of China (Grant No.
447
51190091), and National Key Research and Development Program of China (Grant No.
448
2018YFA0605603). We would like to thank Ming Pan ([email protected]) at
449
Princeton University sharing the Global monthly terrestrial water cycle dataset. We also
450
gratefully acknowledge the hard work and efforts by the editor, Prof. Dr. Emmanouil
451
Anagnostou, and anonymous reviewers for their pertinent and professional comments
452
and suggestions which are greatly helpful for further quality improvement of our
453
manuscript.
454 455
References
456
Berghuijs, W.R., Larsen, J.R., Van Emmerik, T.H.M., Woods, R.A., 2017. A Global
457
Assessment of Runoff Sensitivity to Changes in Precipitation, Potential
458
Evaporation, and Other Factors. Water Resources Research, 53: 8475-8486.
459
Berghuijs, W.R., Woods, R.A., 2016a. Correspondence: Space-time asymmetry
460
undermines water yield assessment. Nature Communications, 7: 11603.
461
DOI:10.1038/ncomms11603 21
462
Berghuijs, W.R., Woods, R.A., 2016b. Correspondence: Space-time asymmetry
463
undermines
water
yield
464
DOI:10.1038/ncomms11603
assessment.
Nature
Communications,
7:
2.
465
Chen, X., Alimohammadi, N., Wang, D., 2013. Modeling interannual variability of
466
seasonal evaporation and storage change based on the extended Budyko
467
framework.
468
DOI:10.1002/wrcr.20493
Water
Resources
Research,
49
(9):
6067-6078.
469
Chen, X., Wei, X., Sun, G., Zhou, P., Zhou, G., 2016. Correspondence: Reply to ‘Space-
470
time asymmetry undermines water yield assessment’. Nature Communications, 7:
471
11604. DOI:10.1038/ncomms11604
472
Choudhury, B., 1999. Evaluation of an empirical equation for annual evaporation using
473
field observations and results from a biophysical model. Journal of Hydrology,
474
216 (1): 99-110.
475
Díaz‐Torres, J., Hernández‐Mena, L., Murillo‐Tovar, M. et al., 2017. Assessment of
476
the modulation effect of rainfall on solar radiation availability at the E arth's
477
surface. 24 (2): 180-190.
478 479
Feng, S., Fu, Q., 2013. Expansion of global drylands under a warming climate. Atmospheric Chemistry and Physics, 13 (6): 10081-10094.
480
Gudmundsson, L., Greve, P., Seneviratne, S.I., 2016. The sensitivity of water
481
availability to changes in the aridity index and other factors-A probabilistic
482
analysis in the Budyko space. Geophysical Research Letters, 43 (13): 6985-6994.
483
DOI:10.1002/2016gl069763
484
Gudmundsson, L., Greve, P., Seneviratne, S.I., 2017. Correspondence: Flawed
485
assumptions compromise water yield assessment. Nat Commun, 8: 14795.
486
DOI:10.1038/ncomms14795
487
Haddeland, I., Heinke, J., Biemans, H. et al., 2014. Global water resources affected by
488
human interventions and climate change. Proceedings of the National Academy of
489
Sciences
490
DOI:10.1073/pnas.1222475110
491
of
the
United
States
of
America,
111
(9):
3251-3256.
Harris, I., Jones, P.D., Osborn, T.J., Lister, D.H., 2014. Updated high-resolution grids 22
492
of monthly climatic observations - the CRU TS3.10 Dataset. International Journal
493
of Climatology, 34 (3): 623-642. DOI:10.1002/joc.3711
494
Hobbins, M.T., 2016. THE VARIABILITY OF ASCE STANDARDIZED
495
REFERENCE EVAPOTRANSPIRATION: A RIGOROUS, CONUS-WIDE
496
DECOMPOSITION AND ATTRIBUTION. Transactions of the Asabe, 59 (2):
497
561-576.
498
Jaramillo, F., Destouni, G., 2014. Developing water change spectra and distinguishing
499
change drivers worldwide. Geophys. Res. Lett., 41 (23): 8377-8386.
500
DOI:10.1002/2014gl061848
501 502 503 504
Jaramillo, F., Destouni, G., 2015. Local flow regulation and irrigation raise global human water consumption and footprint. Sci, 350 (6265): 1248-1251. Karam, H.N., Bras, R.L.J.J.o.H., 2008. Climatological basin-scale Amazonian evapotranspiration estimated through a water budget analysis. 9 (5): 1048-1060.
505
Koster, R.D., Suarez, M.J., 1999. A Simple Framework for Examining the Interannual
506
Variability of Land Surface Moisture Fluxes. Journal of Climate, 12 (7): 1911-
507
1917.
508
Li, D., Pan, M., Cong, Z., Zhang, L., Wood, E., 2013. Vegetation control on water and
509
energy balance within the Budyko framework. Water Resources Research, 49 (2):
510
969-976. DOI:10.1002/wrcr.20107
511
Lin, K., Lv, F., Chen, L. et al., 2014. Xinanjiang model combined with Curve Number
512
to simulate the effect of land use change on environmental flow. Journal of
513
Hydrology, 519: 3142-3152. DOI:10.1016/j.jhydrol.2014.10.049
514
Lin, K., Zhang, Q., Chen, X., 2010. An evaluation of impacts of DEM resolution and
515
parameter correlation on TOPMODEL modeling uncertainty. Journal of
516
Hydrology, 394 (3-4): 370-383.
517
Liu, J., Zhang, Q., Feng, S. et al., 2019. Global attribution of runoff variance across
518
multiple timescales. Journal of Geophysical Research: Atmospheres, 124.
519
DOI:https://doi.org/10.1029/2019JD030539
520
Liu, J., Zhang, Q., Singh, V.P., Shi, P., 2017a. Contribution of multiple climatic
521
variables and human activities to streamflow changes across China. Journal of 23
522
Hydrology, 545: 145-162.
523
Liu, J., Zhang, Q., Singh, V.P. et al., 2018. Hydrological effects of climate variability
524
and vegetation dynamics on annual fluvial water balance in global large river
525
basins.
526
DOI:10.5194/hess-22-4047-2018
Hydrology
and
Earth
System
Sciences,
22
(7):
4047-4060.
527
Liu, J., Zhang, Q., Zhang, Y. et al., 2017b. Deducing Climatic Elasticity to Assess
528
Projected Climate Change Impacts on Streamflow Change across China. Journal
529
of
530
DOI:10.1002/2017jd026701
531 532 533 534
Geophysical
Research-Atmospheres,
122
(19):
10197-10214.
Milly, P.C.D., 1994. Climate, soil water storage, and the average annual water balance. Water Resources Research, 30 (7): 2143-2156. Monteith, J.L., 1965. Evaporation and environment. Symposia of the Society for Experimental Biology, 19: 205-34.
535
Ning, T., Li, Z., Liu, W., 2017. Vegetation dynamics and climate seasonality jointly
536
control the interannual catchment water balance in the Loess Plateau under the
537
Budyko framework. Hydrology and Earth System Sciences, 21 (3): 1515-1526.
538
DOI:10.5194/hess-21-1515-2017
539
Padrón, R.S., Gudmundsson, L., Greve, P., Seneviratne, S.I.J.W.R.R., 2017.
540
Large‐scale controls of the surface water balance over land: Insights from a
541
systematic review and meta‐analysis. 53 (11): 9659-9678.
542
Penman, K.L., 1948. Natural Evaporation from Open Water, Bare Soil and Grass.
543
Proceedings of the Royal Society of London. Series A. Mathematical and Physical
544
Science, 193: 120-145.
545
Potter, N.J., Zhang, L., 2009. Interannual variability of catchment water balance in
546
Australia.
Journal
of
Hydrology,
547
DOI:10.1016/j.jhydrol.2009.02.005
369
(1-2):
120-129.
548
Renner, M., Bernhofer, C., 2012. Applying simple water-energy balance frameworks
549
to predict the climate sensitivity of streamflow over the continental United States.
550
Hydrol. Earth Syst. Sci., 16 (8): 2531-2546. DOI:10.5194/hess-16-2531-2012
551
Solomon, S.J.W.R.R., 1967. Relationship between precipitation, evaporation, and 24
552
runoff in tropical‐equatorial regions. 3 (1): 163-172.
553
Tang, Y., Hooshyar, M., Zhu, T. et al., 2017. Reconstructing annual groundwater
554
storage changes in a large-scale irrigation region using GRACE data and Budyko
555
model. 551: 397-406.
556
Ukkola, A.M., Prentice, I.C., Keenan, T.F. et al., 2016. Reduced streamflow in water-
557
stressed climates consistent with CO2 effects on vegetation. Nature Climate
558
Change, 6 (1): 75-58.
559
Wang, D., 2012. Evaluating interannual water storage changes at watersheds in Illinois
560
based on long‐term soil moisture and groundwater level data. Water Resources
561
Research, 48 (48): 31-40.
562
Wang, D., Alimohammadi, N., 2012. Responses of annual runoff, evaporation, and
563
storage change to climate variability at the watershed scale. Water Resources
564
Research, 48 (5): 5546. DOI:10.1029/2011WR011444
565
Wu, C., Hu, B.X., Huang, G., Zhang, H., 2017. Effects of climate and terrestrial storage
566
on temporal variability of actual evapotranspiration. Journal of Hydrology, 549
567
(549): 388-403.
568
Wu, C., Yeh, P.J.F., Hu, B.X., Huang, G., 2018. Controlling factors of errors in the
569
predicted annual and monthly evaporation from the Budyko framework. Advances
570
in Water Resources, 121: 432-445. DOI:10.1016/j.advwatres.2018.09.013
571
Xing, W., Wang, W., Shao, Q. et al., 2018. Estimating monthly evapotranspiration by
572
assimilating remotely sensed water storage data into the extended Budyko
573
framework across different climatic regions. 567: 684-695.
574
Xu, X., Liu, W., Scanlon, B.R., Zhang, L., Pan, M., 2013. Local and global factors
575
controlling water-energy balances within the Budyko framework. Geophysical
576
Research Letters, 40 (23): 6123-6129. DOI:10.1002/2013gl058324
577
Yang, H., Yang, D., 2011. Derivation of climate elasticity of runoff to assess the effects
578
of climate change on annual runoff. Water Resources Research, 47 (7): 1-12.
579
DOI:10.1029/2010WR009287
580
Yang, H., Yang, D., Hu, Q., 2014. An error analysis of the Budyko hypothesis for
581
assessing the contribution of climate change to runoff. Water Resources Research, 25
582 583 584
50 (12): 9620-9629. Yang, H., Yang, D., Lei, Z., Sun, F., 2008. New analytical derivation of the mean annual water‐energy balance equation. Water Resour. Res., 44 (3): 893-897.
585
Yang, T., Cui, T., Xu, C.Y., Ciais, P., Shi, P., 2017. Development of a new IHA method
586
for impact assessment of climate change on flow regime. Global and Planetary
587
Change, 156. DOI:10.1016/j.gloplacha.2017.07.006
588
Ye, S., Li, H., Li, S. et al., 2015. Vegetation regulation on streamflow intra-annual
589
variability through adaption to climate variations. Geophysical Research Letters,
590
42 (23). DOI:10.1002/2015GL066396
591
Zeng, R., Cai, X., 2015. Assessing the temporal variance of evapotranspiration
592
considering climate and catchment storage factors. Advances in Water Resources,
593
79: 51-60.
594
Zeng, R., Cai, X., 2016. Climatic and terrestrial storage control on evapotranspiration
595
temporal variability: Analysis of river basins around the world. Geophysical
596
Research Letters, 43 (1): 185-195. DOI:10.1002/2015gl066470
597
Zhang, D., Cong, Z., Ni, G., Yang, D., Hu, S., 2015. Effects of snow ratio on annual
598
runoff within the Budyko framework. Hydrology and Earth System Sciences, 19
599
(4): 1977-1992. DOI:10.5194/hess-19-1977-2015
600
Zhang, D., Liu, X., Zhang, Q., Liang, K., Liu, C., 2016a. Investigation of factors
601
affecting intra-annual variability of evapotranspiration and streamflow under
602
different
603
DOI:10.1016/j.jhydrol.2016.10.047
climate
conditions.
Journal
of
Hydrology,
543:
759-769.
604
Zhang, S., Yang, H., Yang, D., Jayawardena, A.W., 2016b. Quantifying the effect of
605
vegetation change on the regional water balance within the Budyko framework.
606
Geophysical Research Letters, 43 (3): 1140-1148. DOI:10.1002/2015GL066952
607
Zhang, Y., Pan, M., Sheffield, J. et al., 2018. A Climate Data Record (CDR) for the
608
global terrestrial water budget: 1984–2010. Hydrology and Earth System Sciences,
609
22 (1): 241-263.
610
Zhou, G., Wei, X., Chen, X. et al., 2015. Global pattern for the effect of climate and
611
land cover on water yield. Nat Commun, 6: 1-9. DOI:10.1038/ncomms6918 26
612 613
Figure captions
614
Fig. 1. The factors affecting evapotranspiration variability from climatic variability
615
(including precipitation and potential evapotranspiration variability), total water storage
616
change and other factors.
617
Fig. 2 Budyko framework (a) without and (b) with consideration of ∆S at annual
618
timescale. The Budyko curves from top to down are derived from Eq. (2) with n = ∞,
619
n = 5, n = 2, n = 1, n = 0.6, n = 0.4. The color bar indicates the counts of overlapping
620
grids.
621
Fig. 3. Comparing assessment E variability assessed by mean absolute deviation (MAD)
622
and that calculated by standard deviation (σ).
623
Fig. 4. Comparing simulated and assessed E variabilities at (a-b) monthly and (c-d)
624
annual scales for terrestrial (i.e., non-oceanic) 0.5º grid points across the globe.
625
Simulated E variabilities are calculated by equation (7) with and without consideration
626
of effects of other factors, while the assessment was evaluated by the standard deviation.
627
The black line is the fitting line and the color bar indicates the counts of overlapping
628
grids.
629
Fig. 5. Comparing simulation accuracy of the analytical method in arid regions (a, c)
630
and humid regions (b, d). The black line is the fitting line and the color bar indicates
631
the counts in overlapping grids.
632
Fig. 6. Modelling errors in the E variability (i.e., simulated values minus assessed
633
values) by latitude. The simulated E variability are evaluated by (a, c) the method
634
proposed in this study and (b, d) the method proposed Zeng and Cai (2015) at monthly 27
635
and annual scale. Black thick lines show the median of errors, and shading shows the
636
quantiles of errors in 30% - 70% and 10% - 90% in the order of darker to lighter shading.
637
Fig. 7. Global patterns for the contributions of (a) P, (b) ∆S, (c) E0 and (d) other
638
factors to monthly variability of E. (e-f) Relationship between the contributions and
639
wetness index (WI, P/E0) for each factor. The red dashed line shows the WI of 0.66,
640
which divides the globe into humid regions (i.e., WI > 0.66) and arid regions (i.e., WI
641
≤ 0.66).
642
Fig. 8. The same as Fig. 7, but for the annual variability of evapotranspiration.
643
Fig. 9. The median contributions of P, ∆S, E0 and n to the E variability for the grids in
644
arid regions, humid regions and globe at (a) monthly and (b) annual scales.
645
Fig. 10. The contributions of P, ∆S, E0 and n to the monthly and annual variability of E
646
in (a, c) arid regions and (b, d) humid regions.
647
Fig. 11. The relationship between monthly precipitation, potential evapotranspiration
648
and actual evapotranspiration in Amazon basin.
649
Fig. 12. Spatial patterns of dominant contributors to the E variability at (a) monthly and
650
(b) annual scale.
28
651 652
Fig. 1. The factors affecting evapotranspiration variability from climatic variability
653
(including precipitation and potential evapotranspiration variability), total water storage
654
change and other factors (e.g., vegetation dynamics and human activities).
655
29
656 657
Fig. 2 Budyko framework without and with consideration of ∆S at (a) monthly and (b)
658
annual scales. The Budyko curves from top to down are derived from Eq. (2) with n =
659
∞, n = 5, n = 2, n = 1, n = 0.6, n = 0.4. The color bar indicates the counts of overlapping
660
grids.
661
30
662 663
Fig. 3. Comparing assessment E variability calculated by mean absolute deviation
664
(MAD) and standard deviation (σ).
665
31
666 667
Fig. 4. Comparing simulated and assessed E variabilities at (a-b) monthly and (c-d)
668
annual scales for terrestrial (i.e., non-oceanic) 0.5º grid points across the globe.
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Simulated E variabilities are calculated by equation (8) with and without consideration
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of effects of other factors, while the assessment was evaluated by the standard deviation.
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The black line is the fitting line and the color bar indicates the counts of overlapping
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grids.
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Fig. 5. Comparing simulation accuracy of the analytical method in arid regions (a, c)
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and humid regions (b, d). The black line is the fitting line and the color bar indicates
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the counts in overlapping grids.
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Fig. 6. Modelling errors in the E variability (i.e., simulated values minus assessed
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values) by latitude. The simulated E variability are evaluated by (a, c) the method
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proposed in this study and (b, d) the method proposed Zeng and Cai (2015) at monthly
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and annual scale. Black thick lines show the median of errors, and shading shows the
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quantiles of errors in 30% - 70% and 10% - 90% in the order of darker to lighter shading.
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Fig. 7. Global patterns for the contributions of (a) P, (b) ∆S, (c) E0 and (d) other
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factors to monthly variability of E. (e-f) Relationship between the contributions and
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dryness index (WI) for each factor. The red dashed line shows the WI of 0.66, which
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divides the globe into humid regions (i.e., WI > 0.66) and arid regions (i.e., WI ≤
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0.66).
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Fig. 8. The same as Fig. 7, but for the annual variability of evapotranspiration.
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Fig. 9. The median contributions of P, ∆S, E0 and other factors to the E variability for
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the grids in arid regions, humid regions and globe at (a) monthly and (b) annual scales.
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Fig. 10. The contributions of P, ∆S, E0 and other factors to the monthly and annual
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variability of E in (a, c) arid regions and (b, d) humid regions.
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Fig. 11. The relationship between monthly precipitation, potential evapotranspiration
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and actual evapotranspiration in Amazon basin.
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Fig. 12. Spatial patterns of dominant contributors to the E variability at (a) monthly and
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(b) annual scale.
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Highlights
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1. We developed a quantitative method to attribute E variability at intra- and inter-
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annual scales. 2. P strengthened E variability in most regions while dampened E variability in extremely humid regions. 3. Catchment characteristics have larger impacts on E variability for humid regions and play a primary role in inter-annual E variability.
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S. Feng, J. Liu, and Q. Zhang designed the study. S. Fen and J. Liu conducted the calculations. S. Feng, J. Liu and Q. Zhang wrote the manuscript with contributions from Y. Zhang, VP Sing, X. Gu and P. Sun. All of the co-authors contributed to scientific interpretations and helped improve the manuscript.
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A global quantitation of factors affecting evapotranspiration
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variability Feng Shuyun1, Jianyu Liu1, Qiang Zhang2,3,4, Yongqiang Zhang5, Vijay P. Singh6, Xihui
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Gu7, Peng Sun8
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1Laboratory
of Critical Zone Evolution, School of Geography and Information Engineering,
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China University of Geosciences, Wuhan 430074, China
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2Key
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Beijing Normal University, Beijing 100875, China
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3State
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University, Beijing 100875, China
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4Faculty
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Management, Beijing Normal University, Beijing 100875, China
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5CSIRO
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6Department
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Engineering, Texas A&M University, College Station, Texas, USA
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7Department
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Geosciences, Wuhan 430074, China;
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8College
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Corresponding author: Qiang Zhang ([email protected]); Jianyu Liu ([email protected])
Laboratory of Environmental Change and Natural Disaster, Ministry of Education,
Key Laboratory of Earth Surface Processes and Resource Ecology, Beijing Normal
of Geographical Science, Academy of Disaster Reduction and Emergency
Land and Water, GPO Box 1700, Canberra ACT 2601, Australia of Biological and Agricultural Engineering and Zachry Department of Civil
of Atmospheric Science, School of Environmental Studies, China University of
of Geography and Tourism, Anhui Normal University, Anhui 241000, China
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Abstract: Scientific viewpoints on the long-term hydrological responses to factors
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other than climatic change remain controversial and yet the impacts of these factors are
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often neglected at the short-term (such as monthly and annual) timescale. We developed
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an analytical method to decompose evapotranspiration (E) variability to the variability
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of precipitation (P), potential evapotranspiration (E0), total water storage change (∆S),
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and catchment characteristics (n), such as vegetation, soil and climate seasonality.
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Global assessment showed that P enhanced E variability in most regions, while
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restrained E variability in some extremely humid regions. E0 controlled monthly E
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variability in most the energy-constrained regions. ∆S had much larger impacts on E
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variability at monthly scale compared to the annual scale, and restrained E variability
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in many arid regions (P/E0 < 0.66). Catchment characteristics had larger impacts on E
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variability in humid regions (P/E0 > 0.66), especially at annual scale. The dominant
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factors of E variability varied with timescales and regions. At a global scale, P and
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catchment characteristics are the dominant factors controlling global E variability at
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monthly and annual scales, respectively; In humid regions, however, the impacts of E0
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on monthly E variability are generally larger than the impacts of precipitation and
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catchment characteristics. We highlight the necessity to consider the impacts of
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catchment characteristics even at the short-term timescales, otherwise the simulation
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and attribution of E variability would be significantly underestimated.
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Keywords: Climate change; Global evapotranspiration; Attribution; Budyko
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framework; Different timescales
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