quantifying the contribution of climate and underlying

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RESEARCH ARTICLE Quantifying the contribution of climate and underlying surface changes to alpine runoff alterations associated with glacier melting Jiali Xin 1 | Xiaoyu Sun 1 | Liu Liu 1,2 | Hao Li 1 | Xingcai Liu 3 | Xiuping Li 4 | Lei Cheng 5,6,7 | Zongxue Xu 8,9 1 College of Water Resources and Civil Engineering, China Agricultural University, Beijing, China 2 Center for Agricultural Water Research in China, China Agricultural University, Beijing, China 3 Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of China, Beijing, China 4 Institute of Tibetan Plateau Research, Chinese Academy of China, Beijing, China 5 State Key Laboratory of Water Resources and Hydropower Engineering Science, Wuhan University, Wuhan, China 6 Hubei Provincial Collaborative Innovation Center for Water Resources Security, Wuhan, China 7 Hubei Provincial Key Lab of Water System Science for Sponge City Construction, Wuhan University, Wuhan, China 8 College of Water Sciences, Beijing Normal University, Beijing, China 9 Beijing Key Laboratory of Urban Hydrological Cycle and Sponge City Technology, Beijing, China Correspondence Liu Liu, College of Water Resources and Civil Engineering, China Agricultural University, Beijing 100083, China. Email: [email protected] Funding information National Natural Science Foundation of China, Grant/Award Numbers: 51961145104, 91647202, 41890822; National Training Program of Innovation and Entrepreneurship for Undergraduates, Grant/Award Number: 202010019052 Abstract Climate variability and underlying surface changes are strongly associated with runoff alterations. The Yarlung Zangbo River Basin (YZRB) is a typical alpine region located in the southeast QinghaiTibet Plateau, where runoff is particularly sensitive and vulnera- ble to climate and environmental changes. Here, we conducted a quantitative assess- ment of the contributions of climate variability and underlying surface changes to runoff alterations from 1966 to 2015 in the upper, middle, and lower regions of the YZRB. The year 1997 was identified as the runoff breakpoint in all three sub-regions, which divided the runoff time series into the baseline period (19661997) and change period (19982015). An adjusted Budyko framework accounting for glacier runoff was devel- oped to conduct a runoff alteration attribution analysis. The results indicated that the increase in runoff in the upper region was dominated by changes in the underlying sur- face and glacier runoff, whose contribution accounted for 59.61 and 49.18%, respec- tively. The runoff increase in the middle and lower regions was mainly attributed to the increase in precipitation, accounting for 39.36 and 129.21% of the total runoff alteration, respectively. Moreover, due to the little variation in vegetation and degradation of per- mafrost in the upper region, increases in runoff might be largely attributed to increases in subsurface runoff caused by the melting of permafrost. In the middle region, in addi- tion to increased precipitation, vegetation degradation had positive effects on runoff increases. The lower region exhibited far higher water consumption rates due to its extensive and dense vegetation coverage accompanied by rising temperature, which resulted in a negative contribution (58.74%) to runoff alteration. Our findings may therefore have important implications for water resource security and sustainable devel- opment in alpine regions. KEYWORDS Budyko, climate change, glacier, permafrost, QinghaiTibet Plateau, runoff 1 | INTRODUCTION Global climate change has significantly altered the hydrological cycle by affecting associated hydrological variables such as precipitation, evapotranspiration, and soil moisture (Allan & Soden, 2008; Fang et al., 2018; Tong et al., 2018; Yang & Yang, 2012; Zhao, Ding, et al., 2019; Zhao, Yang, et al., 2019). However, hydrological dynamics are a complex nonlinear system, whose fluctuations could be Received: 8 September 2020 Revised: 26 January 2021 Accepted: 27 January 2021 DOI: 10.1002/hyp.14069 Hydrological Processes. 2021;35:e14069. wileyonlinelibrary.com/journal/hyp © 2021 John Wiley & Sons Ltd 1 of 26 https://doi.org/10.1002/hyp.14069

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R E S E A R CH A R T I C L E

Quantifying the contribution of climate and underlying surfacechanges to alpine runoff alterations associated with glaciermelting

Jiali Xin1 | Xiaoyu Sun1 | Liu Liu1,2 | Hao Li1 | Xingcai Liu3 | Xiuping Li4 |

Lei Cheng5,6,7 | Zongxue Xu8,9

1College of Water Resources and Civil

Engineering, China Agricultural University,

Beijing, China

2Center for Agricultural Water Research in

China, China Agricultural University, Beijing,

China

3Institute of Geographic Sciences and Natural

Resources Research, Chinese Academy of

China, Beijing, China

4Institute of Tibetan Plateau Research,

Chinese Academy of China, Beijing, China

5State Key Laboratory of Water Resources and

Hydropower Engineering Science, Wuhan

University, Wuhan, China

6Hubei Provincial Collaborative Innovation

Center for Water Resources Security, Wuhan,

China

7Hubei Provincial Key Lab of Water System

Science for Sponge City Construction, Wuhan

University, Wuhan, China

8College of Water Sciences, Beijing Normal

University, Beijing, China

9Beijing Key Laboratory of Urban Hydrological

Cycle and Sponge City Technology, Beijing, China

Correspondence

Liu Liu, College of Water Resources and Civil

Engineering, China Agricultural University,

Beijing 100083, China.

Email: [email protected]

Funding information

National Natural Science Foundation of China,

Grant/Award Numbers: 51961145104,

91647202, 41890822; National Training

Program of Innovation and Entrepreneurship

for Undergraduates, Grant/Award Number:

202010019052

Abstract

Climate variability and underlying surface changes are strongly associated with runoff

alterations. The Yarlung Zangbo River Basin (YZRB) is a typical alpine region located in

the southeast Qinghai–Tibet Plateau, where runoff is particularly sensitive and vulnera-

ble to climate and environmental changes. Here, we conducted a quantitative assess-

ment of the contributions of climate variability and underlying surface changes to runoff

alterations from 1966 to 2015 in the upper, middle, and lower regions of the YZRB. The

year 1997 was identified as the runoff breakpoint in all three sub-regions, which divided

the runoff time series into the baseline period (1966–1997) and change period

(1998–2015). An adjusted Budyko framework accounting for glacier runoff was devel-

oped to conduct a runoff alteration attribution analysis. The results indicated that the

increase in runoff in the upper region was dominated by changes in the underlying sur-

face and glacier runoff, whose contribution accounted for 59.61 and 49.18%, respec-

tively. The runoff increase in the middle and lower regions was mainly attributed to the

increase in precipitation, accounting for 39.36 and 129.21% of the total runoff alteration,

respectively. Moreover, due to the little variation in vegetation and degradation of per-

mafrost in the upper region, increases in runoff might be largely attributed to increases

in subsurface runoff caused by the melting of permafrost. In the middle region, in addi-

tion to increased precipitation, vegetation degradation had positive effects on runoff

increases. The lower region exhibited far higher water consumption rates due to its

extensive and dense vegetation coverage accompanied by rising temperature, which

resulted in a negative contribution (−58.74%) to runoff alteration. Our findings may

therefore have important implications for water resource security and sustainable devel-

opment in alpine regions.

K E YWORD S

Budyko, climate change, glacier, permafrost, Qinghai–Tibet Plateau, runoff

1 | INTRODUCTION

Global climate change has significantly altered the hydrological cycle

by affecting associated hydrological variables such as precipitation,

evapotranspiration, and soil moisture (Allan & Soden, 2008; Fang

et al., 2018; Tong et al., 2018; Yang & Yang, 2012; Zhao, Ding,

et al., 2019; Zhao, Yang, et al., 2019). However, hydrological dynamics

are a complex nonlinear system, whose fluctuations could be

Received: 8 September 2020 Revised: 26 January 2021 Accepted: 27 January 2021

DOI: 10.1002/hyp.14069

Hydrological Processes. 2021;35:e14069. wileyonlinelibrary.com/journal/hyp © 2021 John Wiley & Sons Ltd 1 of 26

https://doi.org/10.1002/hyp.14069

attributed to climate change, and underlying surface changes (Wang

et al., 2008; Zhang, Shoemaker, et al., 2013). Runoff is considered a

basin-scale hydrological cycle outlet and plays an important role in

agricultural irrigation, ecological protection and economic develop-

ment. Importantly, characterizing this phenomenon is critical, to

understand hydrological cycle alterations caused by climate variability

and underlying surface change (Li et al., 2016). Although some studies

have conducted runoff attribution analyses in alpine regions, which

are typically the origin of river headwaters and represent an important

water resource for billions of people (Cong et al., 2017; Feng

et al., 2017; Liu, Chen, et al., 2019), spatio-temporal variations in run-

off and their causes remain unclear due to sparse on-site measure-

ments and the complexity of meltwater runoff generation

mechanisms (Fernández, 1998; Gabbi et al., 2014; Hock &

Holmgren, 2005; Tuteja & Cunnane, 1997; Xing & Zheng, 2003).

Several studies have conducted runoff alteration attribution ana-

lyses using various methods based on different theories. The most

widely used methods can be classified into three types: statistical

methods (Tang et al., 2010; Zhang et al., 2008, 2011; Zhang, Wei,

et al., 2012), hydrological models (Chen et al., 2005; Chiew

et al., 2009; Im et al., 2009; Zhang, Zhang, et al., 2012), and the paired

catchment method (Bi et al., 2009; Brown et al., 2005; Gafur

et al., 2003), each of which possesses its own unique limitations. For

instance, although statistical methods can be implemented relatively

easily, they are known to lack physical foundations and require large

and long-term hydrological and meteorological datasets for runoff

attribution quantitative analysis (Zeng et al., 2014). Hydrological

models facilitate rigorous physical interpretations and play an impor-

tant role in exploring the water cycle. However, due to their relatively

high forcing dataset requirements, conducting studies based on

hydrological models can be rather challenging when the necessary

data is not available (Wang et al., 2013). Moreover, due to the inher-

ent defects of calibration methods, model parameter calibration is not

always accurate, which increases the uncertainty of the simulation

results (Beven & Binley, 1992; Kirchner, 2006). The paired catchment

method is not suitable for large watersheds due to the regional size

restrictions inherent to this approach, which eliminates the effects of

climate change to allow for an effective assessment of the impact of

land cover changes on hydrological processes (Huang et al., 2003).

Compared with the above-described methods, the Budyko framework

requires fewer parameters, which facilitates the estimation of the con-

tributions of climate variability and underlying surface changes to run-

off alteration in a more intuitive way and with a clear physical basis.

According to the Budyko hypothesis (Budyko, 1974), the hydrother-

mal coupling equilibrium equation of the watershed was constructed

to evaluate individual elements of the hydrological cycle and discuss

their response to climate change and the underlying surface. Several

recent studies have validated the Budyko hypothesis and have con-

firmed its outstanding accuracy in large catchments and long-time

scales (He, Qiu, et al., 2019; He, Song, et al., 2019; Li, Su, et al., 2014;

Ning et al., 2016; Xu et al., 2014; Zuo et al., 2014). Therefore, the

Budyko framework was adopted in this study to conduct runoff alter-

ation attribution analyses in the Yarlung Zangbo River Basin (YZRB),

where hydro-meteorological data are scarce and the physical mecha-

nisms of runoff generation are complex (Li, Zhang, et al., 2014; Liu,

Xu, et al., 2019; Zhao et al., 2017). Some studies have applied the

Budyko framework to alpine regions by adjusting the framework

based on the distinctive mechanisms of runoff generation in these

sites, including precipitation, snow melting, and permafrost, among

others. Based on the Budyko framework, Zhang et al. (2015) devel-

oped a Budyko-type equation that accounted for the snow ratio and

water-energy balance to quantify the effects of snow ratios on runoff.

To analyse streamflow responses to frozen ground degradation in the

source region of the Yellow River, Wang et al. (2018) developed a

decomposition method that separated the runoff changes caused by

frozen ground degradation using the Budyko framework. Neverthe-

less, few studies have been conducted to explicitly investigate and

quantify the elasticity and contribution of glacier runoff to the total

runoff in alpine regions, and therefore this topic demands urgent

attention.

The Yarlung Zangbo River (YZR) is the largest river system in the

Qinghai–Tibet Plateau and represents an important channel for the

transportation of moisture (Tian et al., 2001). Thus, this river plays a

significant role in the hydrological cycle of the Asia high mountain

region, which is often referred to as the third pole. Moreover, the

Qinghai–Tibet Plateau is a typical alpine region with fragile ecology;

therefore, the river system in the YZRB is highly sensitive to climate

and environmental changes (Cao et al., 2006; Chaudhary &

Bawa, 2011; Immerzeel et al., 2009). Additionally, the hydro-

meteorological conditions in the YZRB are significantly elevation-

dependent, especially the effect of glacier melting and permafrost

degradation (Wang et al., 2018), which results in much more complex

runoff response mechanisms to climate change than those of other

basins. In recent years, several studies have focused on the changes in

water resources in the YZRB. For example, Cuo et al. (2019) analysed

the variation characteristics of runoff, precipitation, temperature, gla-

ciers, and other factors in the YZRB from 1979 to 2015 as well as the

relationship between each factor and runoff. In a study by

Chen (2012), changes in the YZRB flow from 1961 to 2000 were eval-

uated using the range of variable (RVA) approach. Additionally, due to

the complex topography and large altitude gradient of the YZRB, the

response of hydrological elements to climate change and underlying

surface changes in different regions of this basin are largely heteroge-

neous. Liu et al. (2014) divided the YZRB into five regions and pointed

out that the impacts of land use and climate change on runoff had sig-

nificant spatio-temporal variability. Wang (2015) investigated the tem-

poral and spatial characteristics of precipitation and runoff in the

YZRB from 1973 to 2013, revealing that there were obvious spatial

differences in the impacts of climate and geographical environmental

conditions on the water cycle in the basin. Nevertheless, most of

these studies are limited to the analyses of statistical characteristics

of hydrological and meteorological time series and therefore do not

provide insights into the potential variation mechanisms, making it dif-

ficult to comprehensively evaluate the response of YZRB runoff to cli-

mate variability and underlying surface changes. Therefore, exploring

the spatio-temporal heterogeneity and driving mechanism of runoff

2 of 26 XIN ET AL.

variation in the YZRB is critical to identify dominant influencing fac-

tors in different altitude zones.

Overall, the objectives of this study were: (a) to investigate the

long-term trends in the runoff, precipitation, and potential evapo-

transpiration of different YZRB regions from 1966 to 2015; (b) to

evaluate runoff sensitivity to climate changes (precipitation and

potential evapotranspiration) in different sub-regions, as well as gla-

cier runoff and underlying surface changes based on the adjusted

Budyko framework; and (c) to quantify the contributions of climate

variability and underlying surface changes to runoff variation and fur-

ther identify the driving mechanisms of runoff variation closely associ-

ated with significant altitude gradients. Our study, therefore, provides

important insights into the runoff variations in poorly gauged alpine

regions containing glaciers and permafrost, which may largely influ-

ence downstream water availability. Additionally, this study may shed

light on the impact of climate change on aquatic environments in

high-latitude regions.

2 | MATERIALS AND METHODS

2.1 | Study area

The Yarlung Zangbo River, located in the southern Qinghai–Tibet Pla-

teau (Figure 1a), originates from the glacier in the northern Himalayas

and it flows from west to east through southern Tibet (82–97.12�E

and 28–31.27�N), with a total length of approximately 2000 km and a

total area of �240 000 km2. The YZR is among the highest rivers in

the world, with an altitude span ranging from 133 m to over 7000 m

(Liu, Niu, et al., 2019). This river consists of many tributaries, including

F IGURE 1 Location of the YZRB (a); distribution of the hydrological stations and division of the sub-basins (b)

XIN ET AL. 3 of 26

five first-class tributaries with drainage areas greater than

10 000 km2, including the Lhasa, Nianchu, Parlung Zangbo, Nyang,

and Dogxung Zangbo rivers. In this study, the YZRB was divided into

four regions according to three hydrological stations distributed on

the YZR mainstream (Figure 1b). Due to a lack of in situ measure-

ments in the downstream of the Nuxia hydrological station, only three

regions defined as the upper, middle, and lower regions were selected

in this study (Figure 1b). Our study did not consider the region down-

stream of the Nuxia hydrological station. The runoff in each region

was determined by two adjacent hydrological stations, that is, runoff

in the upper region was determined by the Nugesha hydrological sta-

tion, whereas runoff in the middle and lower regions corresponded to

the differences between the Nugesha and Yangcun hydrological sta-

tions, and the Yangcun and Nuxia hydrological stations, respectively.

Due to the complex terrain and large altitude gradient in the YZRB,

the regional climate varies considerably from the upper region to the

lower region. The annual mean precipitation and runoff gradually

increased from the upper region to the lower region, indicating that the

gradual transition from the westerly region to the monsoon region domi-

nates the variation in precipitation. In the YZRB, significant differences in

climate also result in great spatial heterogeneities of vegetation, which is

closely related to runoff variation. The upper region exhibits the highest

average elevation (4994.2 m) in the entire basin and is therefore mostly

covered by alpine meadows. The middle region has the largest land

build-up in the YZRB and its vegetation is mostly comprised of grass-

lands. In contrast, the lower region receives the largest precipitation vol-

umes and is therefore mainly covered by forests and grasslands.

Furthermore, the YZRB is covered with extensive glaciers, with an area

of 4225 km2 accounting for approximately 2.1% of the total basin,

emphasizing the critical role of glacial meltwater in the basin's hydrologi-

cal dynamics (Yao et al., 2010).

2.2 | Data

Daily gridded data (0.25� × 0.25� spatial resolution) of downward surface

shortwaves, surface pressure, wind speed, and temperature during the

same period as the 1966 to 2015 runoff data collected from the Prince-

ton Global Forcings (http://hydrology.princeton.edu/data/) developed by

Sheffield et al. (2006). Daily precipitation data with a spatial resolution of

0.25� × 0.25� were extracted from the Long-term Land Surface Hydro-

logic Fluxes and States Dataset for China developed by Zhang

et al. (2014), which was verified by the gridded precipitation product of

the China Meteorological Data Service Center (CMA).

The permafrost distribution in the YZRB was obtained from the

National Tibetan Plateau/Third Pole Environment Data Center

(https://data.tpdc.ac.cn/en/data), which was based on the frozen gro-

und map of China and the Map of Glaciers, Frozen Ground, and

Deserts in China (1981–2006) (Wang et al., 2012).

The observed monthly runoff data from 1966 to 2015 at three

hydrological stations used in this study were provided by the Hydrol-

ogy and Water Resources Survey Bureau of the Tibet Autonomous

Region. The three hydrological stations, Nugesha, Yangcun, and Nuxia,

are located on the YZR mainstream from west to east, controlling over

80% of the total runoff in the entire YZRB.

The normalized difference vegetation index (NDVI) data used in this

study were obtained from the Global Inventory Monitoring and Modelling

System (GIMMS) (https://ecocast.arc.nasa.gov/data/pub/gimms/3g.v1/),

which spans from 1982 to 2015 with a spatial resolution of 8 km × 8 km.

Among numerous vegetation index datasets, the GIMMS-NDVI3g dataset

is regarded as one of the best datasets for estimating dynamic changes of

vegetation due to its wide geographical and temporal coverage (Beck &

Goetz, 2011). Moreover, the annual NDVI data used in this study were

obtained using the maximum value composite method (MVCs), which

retained the maximum value of each pixel in each year. The annual maxi-

mum NDVI in the study area is typically reached in summer when the

vegetation is most developed, thus highlighting the intra-annual vegeta-

tion changes in the study site (Holben, 1986; Lv et al., 2014).

2.3 | Methods

2.3.1 | Mann–Kendall nonparametric test formonotonic trend

The Mann–Kendall nonparametric test (Kendall, 1975; Mann, 1945) is

a commonly used nonparametric method to detect trends in hydro-

meteorological time series (He et al., 2017; He, Jiang, et al., 2019;

Sung et al., 2017). Another useful feature of the Mann–Kendall test is

the Kendall slope index, which is an unbiased estimator of the mono-

tonic trend magnitude that was originally developed by Sen (1968)

and later improved upon by Hirsch et al. (1982). Therefore, the runoff,

precipitation, and potential evapotranspiration trends in this study

were examined using the Mann–Kendall test. And the significance

levels of 0.05 and 0.01 were chosen in this study.

2.3.2 | Detection of abrupt change

The determination of change points is critical for the attribution analysis

of runoff variation in this study. For cross-validation and higher accuracy,

three classic methods, including the Pettitt test (Mavromatis &

Stathis, 2011; Pettitt, 1979; Zuo et al., 2014), moving t test (Yin

et al., 2015; Zheng et al., 2007), and the Mann–Kendall test (Goossens &

Berger, 1987; Sneyers, 1975), were used to detect changes in the runoff

in the lower, middle, and upper regions, respectively. Significance levels

of 0.05 and 0.5 were chosen for each method.

2.3.3 | Quantitative attribution of runoff variation

River basin-scale water balance

The long-term water balance equation for a watershed can be

expressed as follows (Yang et al., 2015):

P=R+ ET +ΔS, ð1Þ

4 of 26 XIN ET AL.

where P is the annual average precipitation (mm), R is the annual aver-

age runoff depth, which typically does not include glacier runoff (mm),

ET represents the annual average actual evapotranspiration (mm), and

ΔS is the annual average change of water storage (mm). On the multi-

year average scale (over 10 years), the value of ΔS is likely negligible

(Li, Wang, et al., 2014; Liu et al., 2016; Xue et al., 2013; Zuo

et al., 2014).

Budyko (1974) hypothesized that watershed evapotranspiration

was determined by the water supply (represented by precipitation)

and evaporation capacity (represented by potential evapotranspira-

tion). Several studies have recently begun to focus on implementing

the Budyko hypothesis to characterize the hydrothermal coupling

relationship in a watershed, and many scholars have proposed empiri-

cal equations (Choudhury, 1999; Fu, 1981; Wang & Tang, 2014; Yang

et al., 2008; Zhang et al., 2001, 2004). In this study, the Choudhury–

Yang equation was used to calculate the annual average evapotranspi-

ration as follows:

ET =P× ET0

Pn + ET0nð Þ1=n

, ð2Þ

where ET represents annual average evapotranspiration (mm), P is

annual average precipitation (mm), ET0 represents annual average

potential evapotranspiration (mm), and n is a parameter reflecting the

underlying surface characteristics of the watershed, which is generally

considered to be related to vegetation type and coverage, as well as

soil properties (Donohue et al., 2010; Milly, 1994; Xu et al., 2014). In

this study, the Penman–Monteith method (Allen et al., 1998) was used

for ET0 calculation.

Due to the unique mechanisms of runoff generation in the YZRB,

where the glacier runoff accounts for a non-negligible proportion (Jia

et al., 2008), conventional water balance equations that do not

account for glacier runoff are unsuitable for our study purposes. Thus,

the water balance equation (Equation (1)) was adjusted as follows:

P=Rt 1−rð Þ+ ET, ð3Þ

where Rt represents the total annual average runoff depth

observed by hydrological stations (mm), and r is a coefficient rep-

resenting the proportion of glacier runoff. Thus, Rt(1 − r) is equiva-

lent to R in Equation (1), in which the glacier runoff is subtracted.

Additionally, glacier runoff was defined in this study as a specific

proportion of the melting water from glaciers directly contributing

to the total runoff observed at the hydrological station, rather than

the water derived from glacial melting contributing to YZRB water

storage. Therefore, the annual average change in water storage (ΔS)

can still be neglected at the multi-year average scale. Determina-

tion of r values, which were closely related to temperature varia-

tions and showed significant spatial heterogeneity, is demonstrated

in Section 2.3.4. It should be noted that the runoff defined in the

middle region has already subtracted the runoff from the upper

region, and the runoff defined in the lower region also subtracted

the runoff from the upper and middle regions.

Therefore, by substituting Equation (2) into Equation (3), the

watershed water balance equation can be expressed as follows:

Rt = P−P× ET0

Pn + ET0nð Þ1n

!= 1−rð Þ: ð4Þ

Sensitivity of factors influencing runoff

According to Schaake (1990), the sensitivity of runoff-specific vari-

ables (i.e., P, ET0, r, and n in this study) could be quantified by the elas-

ticity coefficient, which is defined as follows:

εyi =∂Rt

∂yi×yiRt, ð5Þ

where εyi is the elasticity coefficient, and yi represents the specific

influencing factors, which are P, ET0, r, and n in this study.

Assuming that ϕ = ET0/P, the partial derivative of R for each vari-

able (∂Rt/∂yi) can be expressed as:

∂Rt

∂P= 1−

ϕ1+ n

1+ϕnð Þn+1n

!= 1− rð Þ, ð6Þ

∂Rt

∂ET0= −

1

1+ϕnð Þn+1n

!= 1− rð Þ, ð7Þ

∂Rt

∂n= −ET0 ×

nlnϕ+ 1+ϕnð Þln 1 +ϕ−nð Þn2 1 +ϕnð Þn+1n

!= 1− rð Þ, ð8Þ

∂Rt

∂r= P−

ET0

1 +ϕnð Þ1n

!= 1− rð Þ2, ð9Þ

Then, the elasticity coefficients of P, ET0, n, and r can be

expressed, respectively, as follows (Xu et al., 2014):

εP =1+ϕnð Þ 1

1+ n−ϕ1+ n

1+ϕnð Þ 1 +ϕnð Þ1n−ϕh i , ð10Þ

εET0 =1

1+ϕnð Þ 1− 1+ϕ−nð Þ1nh i , ð11Þ

εn =ln 1 +ϕnð Þ+ϕnln 1 +ϕ−nð Þn 1 +ϕnð Þ 1− 1+ϕ−nð Þ1n

h i , ð12Þ

εr =r � P− ET0

1 +ϕnð Þ1n

� �

1− rð Þ � P− P× ET0

Pn + ET0nð Þ1n

� � : ð13Þ

It should be noted that once the runoff breakpoint is determined,

the changes in the contribution of glacier runoff to the total runoff

XIN ET AL. 5 of 26

changes between the two periods could also be calculated by compar-

ing the glacier runoff in the two periods, which renders the same

results as those obtained with the Budyko framework (Equation (13)).

Attribution analysis of runoff variation

Based on the runoff breakpoint determined herein, the study period

was divided into the baseline period (period I) and the change period

(period II). The multi-year average runoff depth of period I is

expressed as R1, whereas that of period II is expressed as R2. The run-

off variation (ΔRt) between period I and period II can be expressed by

the difference in annual average runoff depth before and after the

breaking point (Yang et al., 2015), that is:

ΔRt =R2−R1: ð14Þ

Similarly, changes in multi-year average precipitation potential

(ΔP), evapotranspiration (ΔET0), underlying surface (Δn) , and propor-

tion of glacier runoff (Δr) between the two sub-periods can also be

expressed as follows (Yang et al., 2015):

ΔP=P2−P1, ð15Þ

ΔET0 = ET02−ET01, ð16Þ

Δn= n2−n1, ð17Þ

Δr = r2− r1: ð18Þ

Based on the definition of the elasticity coefficient, the total run-

off variation can be obtained by adding the runoff variations caused

by changes in each variable as follows:

ΔRt = εPRt

PΔP+ εET0

Rt

ET0ΔET0 + εn

Rt

nΔn+ εr

Rt

rΔr + δ: ð19Þ

For a brief demonstration, the previous equation (19) can be sim-

plified indicated below:

ORt =CP +CET0 +Cn +C rð Þ + δ, ð20Þ

where, C_(P), C_(ET0), C_(n),and C_(r) represent the contributions from

changes in climate (P, ET0), underlying surface (n), and glacial melting

(r) to runoff variation, respectively (mm); δ represents the bias

between observed and simulated runoff changes (mm); and O_(Rt) is

the observed change in runoff (mm).

The relative contribution of each variable to the variation in run-

off can be expressed as follows:

RCyi =C_ yið ÞO_ Rtð Þ ×100%, ð21Þ

where yi represents P, ET0, n or r; RC_(yi) represents the relative contri-

bution of yi.

2.3.4 | Determination of glacier runoff proportion

Given that the glacier runoff in the YZRB accounts for a non-

negligible proportion of the total runoff, a coefficient r representing

the proportion of glacier runoff was introduced into the water balance

equation (Equation (1)). It should be noted that the glacier runoff

defined in this study represented a portion of the melting water from

the glaciers, which contributed to the total runoff observed at the

hydrological station. Additionally, the spatio-temporal heterogeneity

of the coefficient r associated with the significant temperature

increases and complex topography of the study site should also be

taken into consideration. However, due to a lack of long-term in situ

measurements of glacier runoff in the YZRB, the values of r for the

three sub-regions were determined based on the glacier runoff simu-

lation results reported by Su et al. (2016) and Zhang, Su, et al. (2013),

using the variable infiltration capacity (VIC) land surface model

coupled with a simple degree-day glacier algorithm, which we will

henceforth refer to as the VIC-glacier model. The initial glacier distri-

bution dataset was obtained from the National Tibetan Plateau/Third

Pole Environment Data Center (http://westdc.westgis.ac.cn/en/data)

and the Randolph Glacier Inventory (http://www.glims.org/RGI/).

Information about the global climate models (GCMs) and a list of the

selected GCMs (Table A1) in the study of Su et al. (2016) are detailed

in Appendix.

Relationship between r and rising temperature

In order to determine the variation characteristics of glacier runoff

induced by rising temperatures closely associated with the upper and

lower region topography, the relationship between the change in tem-

perature (ΔT) and the change in the proportion of glacier runoff (Δr)

was fitted according to the simulation results of glacier runoff during

the 1971–2000, 2011–2040, and 2041–2070 periods (Su et al., 2016;

Zhang, Shoemaker, et al., 2013).The fitting results can be expressed as

follows:

Δr = aΔT + b, ð22Þ

where ΔT represents the temperature change during different

periods; Δr represents the corresponding change in the proportion of

glacier runoff; a represents the fitting coefficient and b represents the

fitting intercept.

Specifically, ΔT and Δr were defined as follows:

ΔT = Tfuture−Tbaseline, ð23Þ

Δr = rfuture−rbaseline, ð24Þ

where Tfuture represents the annual mean temperature during

2011–2040 and 2041–2070 under three representative concentra-

tion pathway (RCP) scenarios (RCP2.6, RCP4.5, RCP8.5) (�C); Tbaselinerepresents the annual mean temperature during 1971–2000 (�C);

rfuture and rbaseline are the future and baseline proportions of glacier

runoff, respectively.

6 of 26 XIN ET AL.

r coefficient calculation

In order to reflect the spatio-temporal heterogeneity of glacier runoff

in the YZRB, r values during periods I and II in the upper, middle, and

lower regions were calculated according to Equation (22) in this study.

Similar to the total runoff defined for the upper, middle, and lower

regions, the glacier runoff for the three sub-regions was defined as

follows:

RgM =RgY −RgU, ð25Þ

RgL =RgW−RgY , ð26Þ

where RgM represents the glacier runoff in the middle region (mm);

RgU represents the glacier runoff in the upper region (mm); RgY rep-

resents the glacier runoff in the region above the Yangcun hydro-

logical station (mm); RgL represents the glacier runoff in the lower

region (mm); RgW and represents the glacier runoff in the whole

basin (mm).

Furthermore, determining the temperature threshold for gla-

cier melting is of great importance for the study of alpine glacier

runoff (Matthews & Hodgkins, 2016). Additionally, due to the

diverse meteorological conditions that glaciers may encounter,

glacier melting can occur over a wide range of air temperatures

(Braithwaite, 1995). According to Ayala et al. (2017), an environ-

mental temperature of −1.5�C, which was adopted in this study

for the YZRB, is much more conducive to glacier ablation in

regions exceeding a 4000 m elevation. Consequently, the coeffi-

cient r in the upper, middle, and lower regions in different periods

could be obtained using the above equations (Equations (22),

(25), and (26)).

2.3.5 | Error estimation of the adjusted Budykoframework

Because the adjusted Budyko framework (Equation (4)) used in this

study is only a first-order approximation, error estimation was con-

ducted to assess its performance.

As described by Yang, Qi, et al. (2014), we wrote the complete

Taylor expansion of Equation (4) as follows:

Rt P1 +ΔP,ET01 +ΔET0,n1 +Δn,r1 +Δrð Þ=Rt P1,ET01 ,n1,r1ð Þ

+ ΔP∂

∂P+ΔET0

∂ET0

∂P+ΔET0

∂ET0+Δn

∂n+Δr

∂r

� �2

Rt P1,ET01 ,n1, r1ð Þ+…,

ð27Þ

where P1 represents the annual average precipitation of period I (mm);

ET01 represents the annual average potential evapotranspiration of

period I (mm); n1 represents the underlying surface characteristics of

period I; r1 represents the proportion of glacier runoff for period I;

ΔP represents the variation of precipitation from period I to period II

(mm); ΔET0 represents the variation of potential evapotranspiration

from period I to period II (mm); Δn represents the variation of the

underlying surface from period I to period II; Δr represents the varia-

tion in glacier melting from period I to period II.

The runoff change caused by the precipitation according to Equa-

tion (27) (C_(ΔP)) can be expressed as follows:

C_ðΔPÞ=ΔP ∂

∂PRt P1,ET01,n1,r1ð Þ+ 1

2!ΔP

∂P+ΔET0

∂ET0+Δn

∂n+Δr

∂r

� �

ΔP∂

∂PRt P1,ET01,n1,r1ð Þ,

ð28Þ

where the third- and higher-order terms of Equation (27) neglected

for the third-order are equal to 3% of the second-order according to

Yang, Yang, and Hu (2014).

Similarly, the runoff change caused by the potential evapotranspi-

ration change (C_(ΔET0)), the underlying surface change (C_(Δn)), and

the glacier melting change (C_(Δr)) can be expressed as follows:

C_ðΔET0Þ=ΔET0∂

∂ET0Rt P1,ET01,n1, r1ð Þ+ 1

2!ΔP

∂P+ΔET0

∂ET0+Δn

∂n+Δr

∂r

� �

ΔET0∂

∂ET0Rt P1,ET01,n1, r1ð Þ,

ð29Þ

C_ðΔnÞ=Δn ∂

∂nRt P1,ET01,n1,r1ð Þ+ 1

2!ΔP

∂P+ΔET0

∂ET0+Δn

∂n+Δr

∂r

� �

Δn∂

∂nRt P1,ET01,n1,r1ð Þ,

ð30Þ

C_ðΔrÞ=Δr ∂∂rRt P1,ET01,n1, r1ð Þ+ 1

2!ΔP

∂P+ΔET0

∂ET0+Δn

∂n+Δr

∂r

� �

Δr∂

∂rRt P1,ET01,n1,r1ð Þ:

ð31Þ

The relative error of the contribution of precipitation change to

the runoff variation (REΔP) was estimated as follows:

REΔP =C_ ΔPð Þ−C_ Pð Þj j

C_ ΔPð Þj j , ð32Þ

where C_(P) represents the contribution of precipitation change to the

runoff variation obtained by the first-order approximation of the

adjusted Budyko framework (mm).

Similarly, the relative error of the contribution of potential evapo-

transpiration change (REΔET0 ), underlying surface change (REΔn), and

glacier melting change (REΔr) were estimated as:

REΔET0 =C_ ΔET0ð Þ−C_ ET0ð Þj j

C_ ΔET0ð Þj j , ð33Þ

REΔn =C_ Δnð Þ−C_ nð Þj j

C_ Δnð Þj j , ð34Þ

REΔr =C_ Δrð Þ−C_ rð Þj j

C_ Δrð Þj j , ð35Þ

XIN ET AL. 7 of 26

where C_(ET0), C_(n) and C_(n) represent the contribution of potential

evapotranspiration change, underlying surface change, and glacier

melting change to the runoff variation obtained by the first-order

approximation of the adjusted Budyko framework, respectively (mm).

3 | RESULTS

3.1 | r coefficient calculation results

According to the simulation results of glacier runoff during the

1971–2000, 2011–2040, and 2041–2070 periods (Su et al., 2016;

Zhang, Shoemaker, et al., 2013) shown in Table 1, the fitting results

were illustrated in Figure 2. The values of fitting coefficient a and

fitting intercept b in Equation (22) were 0.03184 and −0.01237,

respectively. Therefore, with Equations (22), (25), and (26), the coeffi-

cient r in the upper, middle, and lower regions during different periods

could be obtained, which were shown in Tables 2 and 4.

3.2 | Long-term runoff variations and associatedfactors

The statistical characteristics of the hydrological and meteorological

factors of the three regions in the YZRB from 1966 to 2015 are sum-

marized in Table 2. Previous studies have reported that these factors

have opposing impacts on runoff variation, that is, an increase in n,

which represents the characteristics of the underlying surface, includ-

ing vegetation, soil, and topography, would cause a reduction in run-

off, whereas P has the opposite effect (He, Jiang, et al., 2019; He, Qiu,

et al., 2019; Liu, Chen, et al., 2019).

To verify the reliability of the calculated ET0 in this study based

on the Princeton Global Forcings (PGF), a comparison with the ET0

product for China developed by Li et al. (2020) was conducted, which

was calculated based on the China Meteorological Forcing Dataset

(CMFD). As illustrated in Figure 3, the values of R2 of the two datasets

in the upper, middle, lower regions, as well as the entire study area,

were above 0.90. Moreover, the correlations between the two

datasets in the upper, middle, lower, and entire study area were all

statistically significant at a 0.05 level according to the F-test

(Figure 3). The aforementioned results were indicative of a reasonable

performance of calculated ET0 in this study. On the other hand, the

ET0 calculated in this study based on the PGF was generally higher,

especially in the lower region. Relevant studies have indicated that

the measurement of remote sensing data often has some uncer-

tainties in the area covered by glaciers (Lo Vecchio et al., 2018; Wu

et al., 2015), which results in differences between assimilation prod-

ucts. Compared with the CMFD, the downward shortwave radiation

and air temperature of the PGF used for ET0 calculation were both

higher, and the difference between them reached a maximum in the

lower region, which features the largest glacier coverage (Figures A1

and A2), explaining the differences in the estimated ET0 between the

two datasets.

As shown in Table 2, the n, r, and annual average P, Rt, and ET0 of

the upper region during 1966–2015 were 0.80, 0.0635, 400.46,

144.95, and 1294.16 mm, respectively. With decreasing elevation and

increasing temperature, the r, P, Rt, and ET0 values from the upper

region to the middle region showed a consistent increasing trend, with

values of 0.1134, 484.59, 297.04, and 1424.52 mm, respectively.

However, the underlying surface parameter n decreased from 0.80 to

0.56. Furthermore, compared with the 10.07% increase in ET0 and a

30% decrease in n, the r, P, and Rt exhibited much more consistent

and significant increasing magnitudes from the upper region to the

middle region, implying a close positive relationship between r, P, and

Rt in the middle region. With the same decreasing elevation trend and

increasing temperature trend from the upper region to the middle

region, r, P, Rt, and ET0 all exhibited an increasing trend from the

TABLE 1 Changes in temperature (ΔT) and correspondingchanges in glacier runoff proportion (Δr)

Period Scenario ΔT (�C) Δr r

1971–2000 — — — 0.1160

2011–2040 RCP2.6 1.4015 0.0303 0.1463

RCP4.5 1.5744 0.0338 0.1498

RCP8.5 1.6048 0.0338 0.1498

2041–2070 RCP2.6 1.9371 0.0478 0.1638

RCP4.5 2.6929 0.0756 0.1916

RCP8.5 3.5925 0.1035 0.2195

Note: Values of r for the three sub-regions were determined based on the

glacier runoff simulation results by Su et al. (2016).

F IGURE 2 Relationship between the proportion of glacier runoff(r) and temperature changes (ΔT). F represents the F-test statistic,where F > 7.71 represents a significance level of 0.05

8 of 26 XIN ET AL.

middle region to the lower region, with rates of 15.70, 37.27, 151.20,

and 1.61%, respectively, whereas n exhibited a decreasing trend, with

a rate of −69.64%. It is worth noting that, compared with runoff of

144.95 and 297.04 mm respectively in the upper and lower regions,

runoff in the lower regions increased significantly up to 746.15 mm

contributing to the runoff coefficient larger than 1.0, indicating that

glacier runoff in the lower region of the YZRB accounted for a consid-

erable proportion of the runoff, which is consistent with the results

obtained by Liu (1999). Additionally, although runoff and two associ-

ated climate factors (P and ET0) fluctuated slightly due to subtle coef-

ficient variations (<0.3), distinct differences among the variation

characteristics of these factors were observed in the upper, middle,

and lower regions. ET0 in the three regions was steadier than that of

the other elements, with values of 0.02, 0.03, and 0.03, respectively.

However, the P variation coefficients exhibited no differences from

upstream to downstream with a relatively higher value of 0.14,

whereas the variation coefficients of Rt reached a maximum value in

the middle region. Besides, n, r, and the annual average P, Rt, ET0 of

the whole YZRB during 1966–2015 are also summarized in Table 2 as

a reference. In the entire YZRB during 1966–2015, the values of

n and r were 0.60 and 0.1094 respectively, whereas the annual aver-

age P, Rt, and ET0 were 300.72, 516.76, and 1388.73 mm, respec-

tively. Therefore, it is crucial to conduct an in-depth investigation of

the variation trends of hydro-meteorological factors in the YZRB.

The results of the M–K trend test are also shown in Table 2, and

temporal variations in runoff (Rt), precipitation (P), and potential

evapotranspiration (ET0) of the upper, middle, lower regions, as well as

the entire basin, are illustrated in Figure 4, demonstrating that the ET0

of the middle and lower regions had a statistically non-significant

increasing trend (jZcj < 1.96), whereas the ET0 of the upper region

showed a statistically significant increasing trend (jZcj > 1.96).

According to previous studies, increases in vegetation would posi-

tively contribute to increases in ET, which ultimately results in a nega-

tive contribution to runoff. Some studies have indicated that the

vegetation in the entire YZRB has improved in recent decades,

whereas the improvement of vegetation in the middle region was rela-

tively significant, and variations of vegetation in the upper and lower

regions were slight (Li et al., 2019; Liu, Niu, et al., 2019). In the upper

region, the decreasing rate of P and the increasing rate of Rt was

−0.72 and 0.11 mm per year respectively, which were both statisti-

cally non-significant (jZcj < 1.96). Combined with the decrease in P,

increase in ET0, and vegetation improvement in the upper region, it

could be inferred that the increasing trend of Rt in the upper region

might be mainly attributed to glacier melting and permafrost degrada-

tion. In the middle region, P and Rt both exhibited a statistically non-

significant increasing trend (jZcj < 1.96) with the slope of 0.97 and

1.73 mm per year, respectively. Considering the increase of ET0 and

variation in vegetation, such a consistent increasing trend in P and Rt

implied that precipitation was among the dominant factors for the

runoff variation in the middle region. In contrast to the increasing Rt

trend in the upper and middle regions, Rt in the lower region exhibited

a slightly downward trend (jZcj < 1.96) with a negative slope of

−0.91 mm per year, which was opposite to the slight upward trend

(jZcj < 1.96) of P with a positive slope of 1.17 mm per year. The vege-

tation cover of the lower YZRB is mainly composed of grassland and

forest with intensive root systems, which retain water and preserve

the high water content of the underlying surface, positively contribut-

ing to the increase in evaporation and decrease in runoff (Chen

et al., 2014). Regarding the entire YZRB, the increasing Rt, P, and ET0

trends were not statistically significant (jZcj < 1.96).

TABLE 2 Statistical characteristics ofhydrological and meteorological factorsin the YZRB from 1966 to 2015

Region Statistic Rt (mm) P (mm) ET0 (mm) n r

Upper Mean 144.95 400.46 1294.16 0.80 0.0635

Zc 0.27 −1.28 2.54 — —

β 0.11 −0.72 0.82 — —

Coefficients of variation 0.26 0.14 0.02 — —

Middle Mean 297.04 484.59 1424.52 0.56 0.1134

Zc 1.92 1.42 1.81 — —

β 1.73 0.97 0.81 — —

Coefficients of variation 0.27 0.14 0.03 — —

Lower Mean 746.15 665.22 1447.51 0.17 0.1312

Zc −0.92 1.17 0.22 — —

β −0.91 1.14 0.09 — —

Coefficients of variation 0.15 0.14 0.03 — —

YZRB Mean 300.72 516.76 1388.73 0.60 0.1094

Zc 0.65 0.85 1.71 — —

β 0.38 0.59 0.56 — —

Coefficients of variation 0.24 0.14 0.03 — —

Note: jZcj > 2.64 represents the significance level of 0.01; jZcj > 1.96 represents the significance level

of 0.05.

XIN ET AL. 9 of 26

In summary, runoff in the upper region exhibited an increasing

trend coupled with an improvement in vegetation and a decreasing

trend in P, indicating that there were other important factors causing

the increasing in runoff in the upper region. Runoff in the middle

region also exhibited an upward trend, and the simultaneous decreas-

ing vegetation cover and increasing P trends were suggestive of a syn-

ergistic relationship between the underlying surface conditions and

climate change in the middle region. However, Rt in the lower region

exhibited a downward trend, which contradicted the increasing

P trend. Nevertheless, a substantially increased vegetation coverage

consumes more water from the underlying surface (Yang et al., 2015),

which provides a reasonable explanation for the runoff decline and

suggests a more important role of the underlying surface conditions

on runoff variations in the lower region of the YZRB.

3.3 | Determination of the baseline period andchange period for runoff

The determination of the runoff breakpoint involves the rational divi-

sion of the baseline and change periods for attribution analysis of run-

off variation. Nevertheless, breakpoint detection typically entails large

F IGURE 3 Comparison between the ET0 values in the upper (a), middle (b), lower (c) regions, and the whole basin (d). ET0_1 represents theET0 results calculated in this study, whereas ET0_2 represents the ET0 values calculated by Li et al. (2020). F represents the F-test statistic, whereF > 3.86 represents a significance level of 0.05

10 of 26 XIN ET AL.

F IGURE 4 Variations in Rt, P, and ET0 in the upper (a), middle (b), lower (c) regions and the whole basin (d) from 1966 to 2015. Multiyearmean levels of Rt during period Ι (1966–1997) and period II (1998–2015) (e). yRt, yP, and yET0 represent the equations of trendlines with respectto Rt, P, and ET0. Zc represents M–K trend test statistic, where jZcj > 1.96 represents a significance level of 0.05

XIN ET AL. 11 of 26

uncertainties (Wong et al., 2006). Therefore, our study employed the

Pettitt test, moving t test, and Mann–Kendall test to detect abrupt

runoff changes in the three sub-regions of the YZRB. As shown in

Table 3, the abrupt change analysis in the upper region using the

Mann–Kendall test and moving t test were the same as the abrupt

change in annual runoff in 1997, whereas there was no abrupt change

detected by the Pettitt test. In the middle region, different change

points were detected using the three aforementioned methods. The

Pettitt and Mann–Kendall tests indicated that abrupt changes in

annual runoff in the middle region occurred in 1995, whereas the

change point detected by the moving t test occurred in 1997. More-

over, there was no abrupt change in annual runoff detected by any of

the three methods in the lower region. To identify runoff breakpoints

for attribution analysis, abrupt runoff change detection in the entire

YZRB was further conducted based on the measured time series of

runoff at the Nuxia hydrological station, which as identified as the

outlet of the study area. Regarding the moving t test, 1997 was identi-

fied as the change point, which was consistent with the results of Cuo

et al. (2019), Lv and Li (2013), whereas the change point detected by

the Mann–Kendall test appeared in 1996. However, according to the

Pettitt test, there was no abrupt change in the whole basin.

In order to analyse the effect of using different breakpoints on attri-

bution results, we conducted three attribution analyses on runoff alter-

ations when we chose the breakpoint at 1995, 1996, and 1997,

respectively. The attribution results were shown in Tables A2,A3,A4,

indicating that there was no significant impact of three breakpoints on

the results of attribution analysis. Hence, combined with abrupt changes

in runoff in the upper, middle, and entire regions, and to unify the impact

period of climate variability and underlying surface change on runoff vari-

ation in all three sub-regions of the YZRB, 1997 was selected as the

abrupt change point to determine the baseline period and change period

in this study, referring to period I from 1966 to 1997 and period II from

1998 to 2015, respectively.

According to the calculation framework proposed in Section 2.3.4,

the results of the proportions of glacier runoff represented by coeffi-

cient r in the upper, middle, and lower regions during period I and

period II could be quantified as shown in Table 4.

3.4 | Influencing factor sensitivity analysis

Based on the adjusted Budyko framework, the change in runoff cau-

sed by climate variability was decomposed into the impact of precipi-

tation and potential evapotranspiration changes, whereas the impact

of changes in the underlying surface characteristics and glacier melt-

ing on runoff were respectively represented by the integrated param-

eter n defined in Equation (4) and coefficient r. As shown in Table 4,

the statistical characteristics of P, ET0, n, and r during period I and

period II and their corresponding elasticity coefficients exhibited sig-

nificant heterogeneities in the upper, middle, and lower regions. In all

three regions, the Rt and Rt/P in period II were greater than those in

period I. Nevertheless, the value of Rt/P during the two periods in the

lower region was greater than 1.00, further implying that glacial melt-

water played a much more important role in runoff in the lower region

distributed with intensive glaciers. From a whole-basin perspective, a

decrease occurred in ET0/P from the upper region to the lower region,

although Rt/P and Rt exhibited opposite change directions, indicating

that the YZRB becomes gradually wetter with decreased elevation.

Specifically, in the upper region, the ET0/P values during the two

periods were both greater than 3.00, whereas the Rt and P values

were only 0.34 and 0.41, respectively. In addition to a precipitation

volume below 500 mm, the upper region of the YZRB is considered a

typical semi-arid region. From the upper region to the middle region,

the ET0/P values during period I and period II decreased to 3.02 and

2.81, whereas the Rt/P values rose to 0.57 and 0.69, respectively.

With a precipitation of 469.65 and 511.15 mm in periods I and II, the

TABLE 3 Change points detected by three statistical methods

Region Pettitt test Moving t test Mann–Kendall test

Upper — 1997** 1997**

Middle 1995** 1997** 1995**

Lower — — —

YZRB — 1997** 1996**

**Represents the significance level of 0.05.

TABLE 4 Hydro-meteorological characteristics and sensitivity of runoff (Rt) to precipitation (P), potential evapotranspiration (ET0), underlyingsurface (n), and glacier runoff (r) during period I (1966–1997) and period II (1998–2015)

Region Period Rt (mm) P (mm) ET0 (mm) n r Rt/P ET0/P

Elasticity coefficients

εP εET0 εn εr

Upper Period I 134.48 400.97 1285.18 0.82 0.0277 0.34 3.21 1.57 −0.57 −1.48 0.03

Period II 163.56 399.56 1310.13 0.76 0.1161 0.41 3.28 1.50 −0.51 −1.40 0.13

Middle Period I 266.15 469.65 1417.95 0.59 0.1008 0.57 3.02 1.33 −0.47 −1.05 0.11

Period II 351.95 511.15 1436.21 0.53 0.1632 0.69 2.81 1.27 −0.27 −0.91 0.20

Lower Period I 738.71 656.77 1445.89 0.17 0.1328 1.21 2.20 1.01 −0.01 −0.10 0.15

Period II 759.38 680.24 1450.37 0.19 0.1399 1.22 2.13 1.02 −0.02 −0.15 0.16

YZRB Period I 285.66 509.13 1383.01 0.61 0.0960 0.56 2.72 1.34 −0.34 −1.03 0.11

Period II 327.49 530.32 1398.9 0.59 0.1333 0.62 2.64 1.31 −0.31 −0.97 0.15

12 of 26 XIN ET AL.

middle region exhibited a much more typical semi-arid hydro-climatic

characteristics. Transitioning to the lower region from the middle

region, precipitation during the two periods continuously increased to

more than 600 mm, leading to a decrease in ET0/P with values of 2.20

and 2.13. Interestingly, the runoff in the lower region exceeded

700 mm in both periods, which was greater than the precipitation vol-

umes and resulted in a significant increase in R/P, with values of 1.21

and 1.22, respectively, This suggests that the lower region, where

considerable amounts of runoff were contributed by glacier melting, is

an area with typical semi-humid hydro-climatic characteristics. There-

fore, the division of the upper, middle, and lower regions in this study

can reasonably reflect the vertical zonality of the hydro-climate and

elevation dependency of the YZRB, which was the basis for further

analysis of runoff variation attribution in different elevation zones.

The elasticity coefficients of runoff for glacier melting, climate,

and underlying surface factors are also summarized in Table 4. Com-

pared with the relatively smaller elasticity coefficients of ET0, n, and r,

all εP values were the highest in three sub-regions during both two

periods, which translated to the highest runoff sensitivities to precipi-

tation in the entire YZRB. Moreover, the absolute values of εP, εET0,

and εn showed a decreasing trend from the upper region to the lower

region, indicating that runoff in the upper region with highest ET0/P

and lowest Rt/P was the most vulnerable to climate change and

underlying surface evolution. Moreover, although Rt and

P consistently increased from period I to period II in the upper and

middle regions, n opposite variation trend of εP was illustrated, dem-

onstrating that less precipitation corresponded to a higher runoff sen-

sitivity to precipitation in these regions. Although the effect of ET0

and n on runoff variation is opposite to P, εET0, and εn in all three sub-

regions during both two periods exhibited similar variation character-

istics to those of εP. It is worth noting that ET0 increased from period I

to period II in all three sub-regions, whereas the absolute values of

εET0 in the upper and middle regions decreased, indicating that less

potential evapotranspiration corresponded to a greater runoff sensi-

tivity to potential evapotranspiration in these regions. Regarding gla-

cier runoff, all r values maintained a consistent increasing trend with

εr, indicating a greater contribution of meltwater from glaciers induced

by rising temperature. However, the underlying surface changes

induced by parameter n exhibited a different influence on runoff. In

the upper and middle regions, the elasticity of the underlying surface

to runoff represented by εn exhibited a consistent decreasing trend

from period I to period II with that of n. Nonetheless, n and the abso-

lute value of εn in the lower region both increased from period I to

period II. Different changing patterns of εn from upper to lower

regions in the YZRB from period I to period II emphasized the impor-

tance of underlying surface conditions on runoff variations. Compared

with the upper and middle regions, the lower region exhibited larger

forest areas, whose effect on runoff might be amplified during periods

of more abundant precipitation (Wang et al., 2006). Additionally, the

elasticity coefficients of P, ET0, n, and r in the entire YZRB was also

assessed as a reference. The absolute values of εP, εET0, εn, and εr in

the entire YZRB during both periods exhibited similar variation char-

acteristics to those in the upper and middle regions. Specifically, the

absolute values of εP, εET0, and εn in the entire YZRB all decreased

from period I to period II in the same way as in the upper and middle

regions, whereas εr increased. By comprehensively accounting for

elasticity coefficients of precipitation, potential evapotranspiration,

underlying surface, and glacier runoff, the absolute value of εP was

the largest, followed by εn, εET0, and εr, suggesting that runoff in the

YZRB was more sensitive to variations in precipitation than those of

other factors. Additionally, the sensitivity of runoff to precipitation,

potential evapotranspiration, and underlying surface decreased in the

upper, middle, and lower regions, with a gradual decrease in elevation,

whereas the sensitivity of runoff to glacier runoff increased, empha-

sizing the significant role of elevation in alpine areas (Ohmura, 2012;

Yao et al., 2016).

3.5 | Runoff variation attribution analysis

Climate (P and ET0) variability, glacier runoff (r), and underlying surface

(n) changes had different impacts on runoff variation in the upper,

middle, and lower regions (Figure 5). Compared with runoff in

period I, the runoff in period II in the upper, middle, and lower regions

increased by 29.08, 85.80, and 20.67 mm, respectively. To evaluate

the performance of the adjusted Budyko framework in the YZRB, the

relative error between the calculated change in runoff (C_[Rt]) and the

observed change in runoff (O_[Rt]) was calculated and found to be

below 0.4% in all three sub-regions (Figure 5), indicating that the attri-

bution analysis method developed in this study was effective and

accurate for quantifying the impact of various factors on runoff. As

shown in Figure 5, the contributions to runoff in the upper region

associated with changes in precipitation (ΔP), potential evapotranspi-

ration (ΔET0), underlying surface (Δn), and glacier runoff (Δr) were

− 0.81, −1.54, 14.34, and 14.30 mm, which accounted for −2.78,

−5.3, 59.61, and 49.18% of the total runoff increase, respectively. The

corresponding contributions for increased runoff in the middle region

F IGURE 5 Contributions of climate variability (P, ET0), glacierrunoff (r), and underlying surface (n) change to runoff variation

XIN ET AL. 13 of 26

were 33.77, −1.16, 31.24, and 22.34 mm, accounting for 39.36,

−1.36, 36.4, and 26.04%, respectively. In the lower region, contribu-

tions of ΔP, ΔET0, Δn, and Δr to runoff increase were 26.71, −0.04,

−12.14, and 6.16 mm, with corresponding contribution rates of

129.21, −0.17, −55.74, and 29.8%, respectively. These results indi-

cate that changes in the underlying surface represented by n and

changes in glacier melting represented by r dominated the increase of

runoff in the upper region, whereas the change in precipitation had

the most significant impact on runoff increase in the middle and lower

regions, with a non-negligible contribution rate from glacier runoff

over 25%. Compared with the small contribution of ET0, it is worth

noting that the influence of the underlying surface changes was much

greater, with a contribution rate of over 35% in the three sub-regions.

As an important variable reflecting climate change, previous studies

have shown that ET0 plays a key role in the variation of runoff in

alpine areas (Han et al., 2017; Zhang et al., 2016), but some studies

have also pointed out that the underlying surface change showed

larger effects, which warrant closer attention (Feng et al., 2017). A

similar phenomenon highlighting the importance of the underlying

surface was also observed in our study. Specifically, the contribution

rate of the underlying surface change reached 59.61% in the upper

region, which was far more than the precipitation rate contributions.

Additionally, an attribution analysis of the total runoff in the entire

YZRB was also carried out as a reference. The contributions of ΔP,

ΔET0,Δn, and Δr to runoff increases in the entire basin accounted for

39.62, −2.74, 32.32, and 30.94%, which emphasizes the need to fur-

ther investigate the influence of underlying surface change and glacier

melting on alpine runoff.

Because the adjusted Budyko framework (Equation (4)) proposed in

this study is a first-order approximation, error estimation based on Taylor

expansion was further conducted to assess its performance. As shown in

Table 5, the relative errors of the adjusted Budyko framework associated

with precipitation change, potential evapotranspiration change, underly-

ing surface change, and glacier melting change were all small. In the

upper, middle, lower, and whole regions, the relative errors were all less

than 4%. Therefore, the proposed first-order approximation-adjusted

Budyko framework in this study was deemed reliable.

3.6 | Underlying surface variation characteristics

Variations in the underlying surface are mainly caused by changes in

topography, soil, vegetation, and human activities. From the perspec-

tive of a whole river basin-scale over several decades, topography and

TABLE 6 The categorized criteria of the trend of NDVI

Kendall slope Zc value Variation trend of NDVI

≥0.0003 >1.64 Significant improvement

≥0.0003 −1.64 to 1.64 Slight improvement

−0.0003 � 0.0003 −1.64 to 1.64 Stability

≤−0.0003 −1.64 to 1.64 Slight degradation

≤−0.0003 <−1.64 Significant degradation

Note: j Zcj > 1.64 represents the significance level of 0.1.

TABLE 5 Relative errors of adjusted Budyko framework withrespect to precipitation change (REΔP), potential evapotranspirationchange (REΔET0), underlying surface change (REΔn), and glacier meltingchange (REΔr)

Region REΔP (%) REΔET0 (%) REΔn (%) REΔr (%)

Upper 0.88 0.10 1.40 2.53

Middle 0.43 0.82 1.09 2.78

Lower 0.05 3.47 0.58 0.09

YZRB 0.14 0.11 0.33 0.78

F IGURE 6 Spatial variationtrend/significance tests andcorresponding NDVI areapercentage in the YZRB

14 of 26 XIN ET AL.

soil are generally stable, and the impact of human activities in the

YZRB can be neglected due to the pristine nature of this region

(Li et al., 2013; Xiong et al., 2006). Therefore, vegetation dynamics

dominate the variation of the underlying surface in the YZRB. NDVI

has been widely used to investigate dynamic vegetation variations

(Du et al., 2015; Jia et al., 2020; Jiang et al., 2017; Peng et al., 2012).

In this study, 1997 was identified as the runoff breakpoint and was

chosen as the datum point representing the baseline vegetation

period (period I), and the GIMMS-NDVI3g dataset from 1997 to 2015

was used to analyse the variations in vegetation during the change

period (period II) compared to the baseline period (period I) in the

upper, middle, and lower regions. An NDVI variation trend analysis

coupled with a significance test was implemented according to the

method proposed by Li et al. (2019), and the categorized criteria of

the NDVI trend are shown in Table 6. The spatial distribution of the

NDVI variation trend is shown in Figure 6.

In the upper region, the annual maximum NDVI exhibited a

slightly increasing trend with a rate of 0.0001/year (jZcj < 1.64)

(Figure 7a) and the NDVI improvement area accounted for 49.40%

(Figure 6), which is consistent with the results of Liu, Niu, et al. (2019).

F IGURE 7 Variations in vegetation indicated by NDVI in the upper (a), middle (b), and lower (c) regions of the YZRB during 1997–2015. Zcrepresents the Mann–Kendall test statistic and j Zcj > 1.96 represents a significance level of 0.05

XIN ET AL. 15 of 26

Compared with the slightly increasing trend of NDVI in the upper

region, the average maximum NDVI in the middle region showed a

significant decreasing trend with a rate of −0.0015/year (jZcj > 1.64)

(Figure 7b), and the area occupied by vegetation degradation

accounted for 63.82% (Figure 6). In the lower region, the average

maximum NDVI showed a slightly downward trend with a rate of

−0.0005/year (jZcj < 1.64) (Figure 7c), and the area with vegetation

degradation indicated by NDVI occupied 53.03% of the lower region

(Figure 6).

4 | DISCUSSION

4.1 | Implications of climate, underlying surface,and runoff interactions

The upper region had the lowest vegetation coverage in the entire

basin (Jiang et al., 2014). However, according to the results of the

attribution analysis of runoff variation, compared with the middle

and lower regions, the contribution rate of the underlying surface

changes to the increased runoff in the upper region was the largest,

up to 59.61%, demonstrating that the change in the underlying sur-

face played a critical role in the runoff variation in the upper region.

However, according to Section 3.6, the annual maximum NDVI

exhibited a slightly increasing trend with a rate of 0.0001/year

(jZcj < 1.64) and the NDVI improvement area accounted for

49.40%. Obviously, due to slight changes in vegetation in the upper

region, other factors associated with the underlying surface in the

upper region must be responsible for such a great contribution to

the increased runoff from period I to period II. As shown in

Figure 8, the upper region has the largest coverage of permafrost

(43304.64 km2) in the YZRB. In recent years, the degradation of

permafrost on the Qinghai–Tibet Plateau has been significantly

intensified due to global warming (Cheng & Wu, 2007), resulting in

gradual thawing of permafrost and changing the thermal-moisture

dynamics of the active layer (Zhang et al., 2019). It could be

deduced that the change in the underlying surface in the upper

region may be related to the melting of permafrost, and the melting

and infiltration of permafrost would increase the subsurface runoff

(Liu et al., 2005; Ye et al., 2009). Additionally, the melting of perma-

frost could lead to an increase in soil water permeability

(St. Jacques & Sauchyn, 2009). Clark et al. (2001), reported that the

melting and infiltration of permafrost in permafrost regions would

increase the replenishment of precipitation to groundwater storage

to some extent. Therefore, the melting of permafrost may also

result in a reduction of direct recharge to runoff by precipitation,

causing the contribution of precipitation to runoff to be signifi-

cantly less than that of the underlying surface. Furthermore, the

contribution of glacier runoff cannot be ignored, which accounts

for 49.18% of the variation in total runoff. With significant temper-

ature increases, the proportion of glacier runoff (r) in the upper

region exhibited a consistently increasing trend with the largest

increasing magnitude in the three sub-regions from period Ι to

period II, while precipitation remained nearly constant, resulting in

a high contribution rate of glacier runoff. Consequently, the

increase in runoff during the changing period in the upper region of

F IGURE 8 The distribution of permafrost in the YZRB was obtained from the National Tibetan Plateau Data Center (http://data.tpdc.ac.cn/zh-hans/), which was based on the frozen ground map of China and a map of the glaciers, frozen ground, and deserts in China (Wang et al., 2012)

16 of 26 XIN ET AL.

the YZRB should be mainly attributed to the increase in under-

ground runoff caused by the melting of permafrost and glaciers

associated with rising temperatures.

In the middle region, the vegetation types were mainly shrubs

and grasslands. What's more, in terms of Section 3.6, the average

maximum NDVI in the middle region showed a significant decreasing

trend with a rate of −0.0015/year (jZcj > 1.64), and the area occupied

by vegetation degradation accounted for 63.82%. Previous studies

have shown that the degradation of vegetation promotes the forma-

tion of surface runoff, which in turn increases the total runoff

(Bosch & Hewlett, 1982; Lin & Wei, 2008; Ruprecht &

Schofield, 1991a, 1991b). Furthermore, as shown in Table 2, precipita-

tion exhibited an upward trend in the middle region, which dominated

the increase in runoff with the largest contribution rate of 39.36%.

Moreover, glacier runoff in this region also played an important role in

the increase in runoff. However, compared with the upper region, the

contribution rate of glacier runoff decreased from 49.18% to 26.04

due to an increase in precipitation of up to 10% from period Ι to

period II. due to the relatively smaller cover area of permafrost in the

middle region (15426.61 km2), the contribution rate of the underlying

surface represented by n also decreased from 59.61 to 36.4%.

In the lower region, vegetation was mainly covered by forest and

grassland, with considerable water consumption from transpiration.

Combined with the vegetation variation results in Section 3.6, the

average maximum NDVI showed a slightly downward trend with a

rate of −0.0005/year (jZcj < 1.64), and the area with vegetation degra-

dation indicated by NDVI occupied 53.03% of the lower region. The

slight decline of NDVI reduced the water resistance of surface vegeta-

tion to some extent, which led to an increase in runoff. However,

compared to the upper and middle regions, the vegetation coverage

of the lower region was much larger and denser, leading to more

water consumption than water yield with increasing temperature due

to vegetation degradation. Additionally, the area of permafrost in the

lower region (5702.61 km2) was much smaller than that of forest and

grassland, indicating that the contribution of the underlying surface

change to runoff could be mainly attributed to the variations in vege-

tation. Therefore, the contribution rate of the underlying surface (n)

was negative, with a value of −58.74%. Similar to the upper and mid-

dle regions, the increase in glacier runoff made a positive contribution

to the total runoff, accounting for 29.8%. Moreover, the precipitation

in the lower region was the largest of all sub-regions and therefore

dominated the increase in runoff, with the greatest contribution rate

of up to 129.21%.

4.2 | Limitations and uncertainties

There were still some limitations and uncertainties in this study. First,

in terms of sensitivity analysis, lower climate variable values cor-

responded to greater runoff sensitivity in the lower, middle and upper

regions. Similar results were also obtained in other studies, but the

physical mechanisms for this phenomenon remain unclear. Wu

et al. (2017) reported that during the high-flow period, runoff was

more sensitive to precipitation in all 17 catchments of the Loess Pla-

teau. Lee and Yeh (2019) demonstrated that in the Lanyang River

basin, although the corresponding sensitivity of runoff was greater

with greater P, the sensitivity of runoff to ET0 exhibited the opposite

trend. Second, due to the complex vertical zonality of permafrost and

glacier melting mechanisms (Fernández, 1998; Gabbi et al., 2014;

Hock & Holmgren, 2005; Tuteja & Cunnane, 1997; Xing &

Zheng, 2003), the influence of meltwater from permafrost and glaciers

on runoff variation at different elevation zones should be elaborately

discussed in future. Third, the quantitative estimations in this study

were based on the assumption that the variations in climate and

underlying surface are independent. Nevertheless, in natural catch-

ments, these two factors are inter-related (Zeng et al., 2015; Zheng

et al., 2009). Furthermore, the simulation results by Su et al. (2016)

and Zhang, Su, et al. (2013) used in this study to derive the values of

r for the three sub-regions also had uncertainties associated with the

hydrologic model parameters. According to Zhang, Su, et al. (2013),

the model uncertainties associated with temperature change (from

0 to 1.1�C/100 m) were generally within 3%, whereas a 1 unit

(mm �C−1 day−1) increase in the degree-day factor for ice melt could

cause a 5% increase in glacier runoff. Given that the VIC-glacier model

has been calibrated and validated with forcing data and runoff data

based on long-term observations, the uncertainty of runoff prediction

caused by climate change prediction is much greater than that of the

hydrological model itself. Finally, the results of glacier runoff simula-

tion in the study of Su et al. (2016) and Zhang, Shoemaker,

et al. (2013) did not show an obvious tipping point and continued to

increase. According to Huss and Hock (2018), the tipping point for

glacier runoff in the YZRB will be reached in the near future (approxi-

mately by the 2030s). Zhao, Ding, et al. (2019) and Zhao, Yang,

et al. (2019) also projected a constant decrease in glacier runoff in the

study region from the 1970s to the 2090s. The reason why the glacier

runoff in the study of Su et al. (2016) continued to increase in the

future might be that they used the delta method to obtain future forc-

ing and did not continuously simulate future changes. This might

affect the accuracy of the results of r, which was derived from the

results of the glacier runoff simulation by Su et al. (2016) and Zhang,

Shoemaker, et al. (2013).

5 | CONCLUSIONS

In this study, long-term trends in the runoff, precipitation and poten-

tial evapotranspiration of the upper, middle and lower regions of the

YZRB from 1966 to 2015 were analysed, and the attribution analysis

within an adjusted Budyko framework, which subtracted the glacier

runoff from the total runoff, was applied to quantitatively estimate

the relative contributions of climate variability, glacier melting and

underlying surface change to runoff variation in each region. Based on

GIMMS NDVI data from 1997 to 2015, the spatial dynamic variations

of vegetation were investigated to further explore the driving mecha-

nism of runoff variation associated with hydro-meteorological factors.

The following are the key conclusions of this study:

XIN ET AL. 17 of 26

1. During the 1966–2015 period, runoff, precipitation and potential

evapotranspiration in all three sub-regions mostly exhibited an

increasing trend except for precipitation in the upper region and

runoff in the lower region, which exhibited a decreasing trend.

2. Runoff in all three sub-regions was most sensitive to precipitation,

followed by the underlying surface, potential evapotranspiration

and glacier runoff. Furthermore, consistent with the decrease in

elevation, the sensitivity of runoff to precipitation, potential

evapotranspiration and underlying surface all decreased along the

upper, middle and lower regions, whereas the sensitivity of runoff

to glacier melting represented by the coefficient r exhibited the

opposite trend.

3. To unify the impact period of climate variability and underlying

surface change on runoff, the year 1997 was selected as the

breakpoint to determine the baseline period and change period

according to the abrupt change detection results. From the base-

line period to the change period, the runoff increased in all three

sub-regions. According to the adjusted Budyko framework, the

dominant factor contributing to the increase in runoff in the upper

region was the underlying surface change, with a contribution of

59.61%. The runoff increase in the middle and lower regions was

mainly attributed to the increase in precipitation, accounting for

39.36 and 129.21%, respectively.

4. Due to the little variation in vegetation and the increasing degrada-

tion of permafrost in the upper region, the increase in runoff may

be mainly attributed to the increase in underground runoff caused

by the melting of permafrost. In the middle region, in addition to

the increase in precipitation, the significant decrease in vegetation

also had a positive effect on runoff increase. In the lower region,

the increase in runoff was mainly caused by the increase in precipi-

tation. Therefore, the positive contribution of glacial runoff to the

total runoff variation in the Yarlung Zangbo River Basin empha-

sizes the importance of investigating the mechanisms by which

glacier meltwater influences runoff variations in alpine regions.

ACKNOWLEDGEMENTS

This work was jointly supported by the National Natural Science

Foundation of China (Grant Nos. 51961145104, 91647202, and

41890822) and National Training Program of Innovation and Entre-

preneurship for Undergraduates (Grant No. 202010019052).

CONFLICT OF INTEREST

The authors declare no conflicts of interest.

DATA AVAILABILITY STATEMENT

The Princeton Global Forcings that support the findings of this study

are available in the Terrestrial Hydrology Research Group at Princeton

University at http://hydrology.princeton.edu/data/. Daily precipita-

tion data extracted from the Long-term Land Surface Hydrologic

Fluxes and States Dataset for China are available at the Institute of

Geographic Sciences and Natural Resources Research, Chinese Acad-

emy of Sciences, by contacting [email protected] or tangqh@igsnrr.

ac.cn. The distribution of permafrost in the YZRB is available in the

National Tibetan Plateau/Third Pole Environment Data Center at

https://data.tpdc.ac.cn/en//, with reference number DOI: https://doi.

org/10.11888/Geocry.tpdc.270038. The observed monthly runoff

data from the three hydrological stations are available from the

Hydrology and Water Resources Survey Bureau of the Tibet Autono

mous Region, which are not publicly available due to privacy

restrictions.

ORCID

Liu Liu https://orcid.org/0000-0002-4915-206X

Lei Cheng https://orcid.org/0000-0002-5298-9573

REFERENCES

Allan, R. P., & Soden, B. J. (2008). Atmospheric warming and the amplifica-

tion of precipitation extremes. Science, 321(5895), 1481–1484.https://doi.org/10.1126/science.1160787

Allen, R. G., Pereira, L. S., Raes, D., & Smith, M. (1998). Crop evapotranspira-

tion. Guidelines for computing crop water requirements (p. 300). United

Nations Food and Agriculture Organization, Irrigation and drainage

paper.

Ayala, A., Pellicciotti, F., MacDonell, S., McPhee, J., & Burlando, P. (2017).

Patterns of glacier ablation across North-Central Chile: Identifying the

limits of empirical melt models under sublimation-favorable conditions.

Water Resources Research, 53(7), 5601–5625. https://doi.org/10.

1002/2016WR020126

Beck, P. S. A., & Goetz, S. J. (2011). Satellite observations of high northern lati-

tude vegetation productivity changes between 1982 and 2008: Ecological

variability and regional differences. Environmental Research Letters, 6(4),

045501. https://doi.org/10.1088/1748-9326/6/4/045501

Beven, K., & Binley, A. (1992). The future of distributed models—Model

calibration and uncertainty prediction. Hydrological Processes, 6,

279–298. https://doi.org/10.1002/hyp.3360060305Bi, H., Liu, B., Wu, J., Yun, L., Chen, Z., & Cui, Z. (2009). Effects of precipi-

tation and land use on runoff during the past 50 years in a typical

watershed in Loess Plateau, China. International Journal of Sediment

Research, 24(3), 352–364. https://doi.org/10.1016/S1001-6279(10)

60009-1

Bosch, J. M., & Hewlett, J. D. (1982). A review of catchment experiments

to determine the effect of vegetation changes on water yield and

evapotranspiration. Journal of Hydrology, 55(1), 3–23. https://doi.org/10.1016/0022-1694(82)90117-2

Braithwaite, R. J. (1995). Positive degree-day factors for ablation on the

Greenland ice sheet studied by energy-balance modelling. Journal of

Glaciology, 41(137), 153–160. https://doi.org/10.3189/S0022143000017846

Brown, A. E., Zhang, L., McMahon, T. A., Western, A. W., & Vertessy, R. A.

(2005). A review of paired catchment studies for determining changes

in water yield resulting from alterations in vegetation. Journal of

Hydrology, 310(1–4), 28–61. https://doi.org/10.1016/j.jhydrol.2004.

12.010

Budyko, M. I. (1974). Climate and life. Academic Press.

Cao, J., Qin, D., Kang, E., & Li, Y. (2006). River discharge changes in the

Qinghai–Tibet Plateau. Chinese Science Bulletin 51, 5(594–600).https://dx.doi.org/10.1007/s11434-006-0594-6.

Chaudhary, P., & Bawa, K. S. (2011). Local perceptions of climate change

validated by scientific evidence in the Himalayas. Biology Letters, 7(5),

767–770. https://doi.org/10.1098/rsbl.2011.0269Chen, H. (2012). Assessment of hydrological alterations from 1961 to

2000 in the Yarlung Zangbo River, Tibet. Ecohydrology & Hydrobiology,

12(2), 93–103. https://doi.org/10.2478/v10104-012-0009-zChen, J., Li, X., & Zhang, M. (2005). Simulating the impacts of climate varia-

tion and land-cover changes on basin hydrology: A case study of the

18 of 26 XIN ET AL.

Suomo basin. Science in China Series D: Earth Sciences, 48(9),

1501–1509. https://doi.org/10.1360/03yd0269Chen, R., Yang, Y., Han, C., Liu, J., Kang, E., Song, Y., & Liu, Z. (2014). Field

experimental research on hydrological function over several typical

underlying surfaces in the cold regions of western China. Advances in

Earth Science, 29(4), 507–514.Cheng, G., & Wu, T. (2007). Responses of permafrost to climate change

and their environmental significance, Qinghai–Tibet Plateau. Journal ofGeophysical Research: Earth Surface, 112(F2). https://doi.org/10.1029/

2006JF000631

Chiew, F. H. S., Teng, J., Vaze, J., Post, D. A., Perraud, J. M.,

Kirono, D. G. C., & Viney, N. R. (2009). Estimating climate change

impact on runoff across Southeast Australia: Method, results, and

implications of the modeling method. Water Resources Research, 45

(10). https://doi.org/10.1029/2008WR007338

Choudhury, B. J. (1999). Evaluation of an empirical equation for annual

evaporation using field observations and results from a biophysical

model. Journal of Hydrology, 216(1–2), 99–110. https://doi.org/10.

1016/S0022-1694(98)00293-5

Clark, I. D., Lauriol, B., Harwood, L., & Marschner, M. (2001). Groundwater

contributions to discharge in a permafrost setting, Big Fish River,

N.W.T., Canada. Arctic, Antarctic, and Alpine Research, 33(1), 62–69.https://doi.org/10.2307/1552278

Cong, Z., Shahid, M., Zhang, D., Lei, H., & Yang, D. (2017). Attribution of

runoff change in the alpine basin: A case study of the Heihe Upstream

Basin, China. Hydrological Sciences Journal, 62(6), 1013–1028. https://doi.org/10.1080/02626667.2017.1283043

Cuo, L., Li, N., Liu, Z., Ding, J., Liang, L., Zhang, Y., & Gong, T. (2019).

Warming and human activities induced changes in the Yarlung

Tsangpo basin of the Tibetan plateau and their influences on

streamflow. Journal of Hydrology: Regional Studies, 25, 100625.

https://doi.org/10.1016/j.ejrh.2019.100625

Donohue, R. J., Roderick, M. L., & McVicar, T. R. (2010). Can dynamic veg-

etation information improve the accuracy of Budyko's hydrological

model? Journal of Hydrology, 390(1–2), 23–34. https://doi.org/10.

1016/j.jhydrol.2010.06.025

Du, J., Shu, J., Yin, J., Yuan, X., Jiaerheng, A., Xiong, S., … Liu, W. (2015).

Analysis on spatio-temporal trends and drivers in vegetation growth

during recent decades in Xinjiang, China. International Journal of

Applied Earth Observation and Geoinformation, 38, 216–228. https://doi.org/10.1016/j.jag.2015.01.006

Fang, J., Kong, F., Fang, J., & Zhao, L. (2018). Observed changes in hydrolog-

ical extremes and flood disaster in Yangtze River Basin: Spatial–temporal variability and climate change impacts. Natural Hazards, 93(1),

89–107. https://doi.org/10.1007/s11069-018-3290-3Feng, A., Li, Y., Gao, J., Wu, S., & Feng, A. (2017). The determinants of

streamflow variability and variation in Three-River Source of China:

Climate change or ecological restoration? Environmental Earth Sciences,

76(20), 696. https://doi.org/10.1007/s12665-017-7026-6

Fernández, A. (1998). An energy balance model of seasonal snow evolu-

tion. Physics and Chemistry of the Earth, 23(5), 661–666. https://doi.org/10.1016/S0079-1946(98)00107-4

Fu, B. (1981). On the calculation of the evaporation from land surface.

Scientia Atmospherica Sinica, 5(1), 23–31.Gabbi, J., Carenzo, M., Pellicciotti, F., Bauder, A., & Funk, M. (2014). A

comparison of empirical and physically based glacier surface melt

models for long-term simulations of glacier response. Journal of Glaci-

ology, 60(224), 1140–1154. https://doi.org/10.3189/2014JoG14J011Gafur, A., Jensen, J. R., Borggaard, O., & Petersen, L. (2003). Runoff and losses

of soil and nutrients from small watersheds under. Shifting cultivation

(Jhum) in the Chittagong Hill Tracts of Bangladesh. Journal of Hydrology,

279, 292–309. https://doi.org/10.1016/S0022-1694(03)00262-2Goossens, C., & Berger, A. (1987). How to recognize an abrupt climatic

change. In Abrupt climatic change: Evidence and implications

(pp. 31–46). Springer.

Han, L., Song, K., Zhang, W., Liu, L., & Jiang, H. (2017). Temporal and spa-

tial variations of hydrological factors in the source area of the Yangtze

River and its responses to climate change. Mountain Research, 35(2),

129–141.He, Y., Jiang, X., Wang, N., Zhang, S., Ning, T., Zhao, Y., & Hu, Y. (2019).

Changes in mountainous runoff in three inland river basins in the arid

Hexi Corridor, China, and its influencing factors. Sustainable Cities and

Society, 50, 101703. https://doi.org/10.1016/j.scs.2019.101703

He, Y., Qiu, H., Song, J., Zhao, Y., Zhang, L., Hu, S., & Hu, Y. (2019). Quanti-

tative contribution of climate change and human activities to runoff

changes in the Bahe River watershed of the Qinling Mountains, China.

Sustainable Cities and Society, 51, 101729. https://doi.org/10.1016/j.

scs.2019.101729

He, Y., Song, J., Hu, Y., Tu, X., & Zhao, Y. (2019). Impacts of different

weather conditions and land use change on runoff variations in the

Beiluo River Watershed, China. Sustainable Cities and Society, 50,

101674. https://doi.org/10.1016/j.scs.2019.101674

He, Y., Tian, P., Mu, X., Gao, P., Zhao, G., Wang, F., & Li, P. (2017). Changes

in daily and monthly rainfall in the Middle Yellow River, China. Theoret-

ical and Applied Climatology, 129(1–2), 139–148. https://doi.org/10.1007/s00704-016-1763-4

Hirsch, R. M., Slack, J. R., & Smith, R. A. (1982). Techniques of trend analy-

sis for monthly water-quality data. Water Resources Research, 18,

107–121.Hock, R., & Holmgren, B. (2005). A distributed surface energy-balance

model for complex topography and its application to Storglaciären,

Sweden. Journal of Glaciology, 51(172), 25–36. https://doi.org/10.

3189/172756505781829566

Holben, B. N. (1986). Characteristics of maximum-value composite images

from temporal AVHRR data. International Journal of Remote Sensing, 7

(11), 1417–1434. https://doi.org/10.1080/01431168608948945Huang, M., Zhang, L., & Gallichand, J. (2003). Runoff responses to affores-

tation in a watershed of the Loess Plateau, China. Hydrological Pro-

cesses, 17, 2599–2609. https://doi.org/10.1002/hyp.1281Huss, M., & Hock, R. (2018). Global-scale hydrological response to future

glacier mass loss. Nature Climate Change, 8(2), 135–140. https://doi.org/10.1038/s41558-017-0049-x

Im, S., Kim, H., Kim, C., & Jang, C. (2009). Assessing the impacts of land

use changes on watershed hydrology using MIKE SHE. Environmen-

tal Geology, 57, 231–239. https://doi.org/10.1007/s00254-008-

1303-3

Immerzeel, W. W., Droogers, P., De Jong, S. M., & Bierkens, M. F. P.

(2009). Large-scale monitoring of snow cover and runoff simulation in

Himalayan river basins using remote sensing. Remote Sensing of Envi-

ronment, 113(1), 40–49. https://doi.org/10.1016/j.rse.2008.08.010Jia, J., Lv, S., & Wang, Z. (2008). Characteristics of water resources in the

Yarlung Zangbo River Basin. Yangtze River, (17), 71–72+81.Jia, L., Li, Z., Xu, G., Ren, Z., Li, P., Cheng, Y., … Yu, S. (2020). Dynamic

change of vegetation and its response to climate and topographic fac-

tors in the Xijiang River Basin, China. Environmental Science and Pollu-

tion Research. 27, 11637–11648. https://doi.org/10.1007/s11356-

020-07692-w

Jiang, L., Feng, W., & Guo, B. (2014). Analysis of dynamic monitoring of

vegetation change and the correlation with precipitation factor in

Yarlung Tsangpo River Basin during the past 13 years. Resources and

Environment in the Yangtze Basin, 23(11), 1610–1619.Jiang, L., Jiapaer, G., Bao, A., Guo, H., & Ndayisaba, F. (2017). Vegetation

dynamics and responses to climate change and human activities in

Central Asia. Science of the Total Environment, 599–600, 967–980.https://doi.org/10.1016/j.scitotenv.2017.05.012

Kendall, M. G. (1975). Rank correlation measures. Charles Griffin.

Kirchner, J. W. (2006). Getting the right answers for the right reasons:

Linking measurements, analyses, and models to advance the science of

hydrology. Water Resources Research, 42(3). W03S04. https://doi.org/

10.1029/2005WR004362

XIN ET AL. 19 of 26

Lee, C., & Yeh, H. (2019). Impact of climate change and human activities

on streamflow variations based on the Budyko framework. Water, 11

(10). 2001. https://doi.org/10.3390/w11102001

Li, B., Su, H., Chen, F., Li, H., Zhang, R., Tian, J., … Rong, Y. (2014). Separa-

tion of the impact of climate change and human activity on streamflow

in the upper and middle reaches of the Taoer River, northeastern

China. Theoretical and Applied Climatology, 118(1–2), 271–283.https://doi.org/10.1007/s00704-013-1032-8

Li, F., Xu, Z., Feng, Y., Liu, M., & Liu, W. (2013). Changes of land cover in

the Yarlung Tsangpo River basin from 1985 to 2005. Environmental

Earth Sciences, 68(1), 181–188. https://doi.org/10.1007/s12665-012-1730-z

Li, F., Zhang, Y., Xu, Z., Liu, C., Zhou, Y., & Liu, W. (2014). Runoff predic-

tions in ungauged catchments in southeast Tibetan Plateau. Journal of

Hydrology, 511, 28–38. https://doi.org/10.1016/j.jhydrol.2014.01.014Li, H., Liu, L., Liu, X., Li, X., & Xu, Z. (2019). Greening implication inferred

from vegetation dynamics interacted with climate change and human

activities over the Southeast Qinghai–Tibet Plateau. Remote Sensing,

11(20), 2421. https://doi.org/10.3390/rs11202421

Li, Q., Cheng, L., Ye, L., Liu, P., & Xiong, L. (2020). Long-term land surface

evaporation and its changes estimated by the generalized complemen-

tary principle in China. Journal of Water Resources Research, 9(3),

259–269. https://doi.org/10.12677/JWRR.2020.93027

Li, X., Wang, L., Chen, D., Yang, K., & Wang, A. (2014). Seasonal evapo-

transpiration changes (1983–2006) of four large basins on the Tibetan

Plateau. Journal of Geophysical Research, 119, 13079–13095. https://doi.org/10.1002/2014JD022380

Li, Y., Liu, C., Zhang, D., Liang, K., Li, X., & Dong, G. (2016). Reduced runoff

due to anthropogenic intervention in the Loess Plateau, China. Water,

8(10). 458. https://doi.org/10.3390/w8100458

Lin, Y., & Wei, X. (2008). The impact of large-scale forest harvesting on

hydrology in the Willow watershed of Central British Columbia. Jour-

nal of Hydrology, 359(1), 141–149. https://doi.org/10.1016/j.jhydrol.2008.06.023

Liu, B., Yang, D., Ye, B., & Berezovskaya, S. (2005). Long-term open-water

season stream temperature variations and changes over Lena River

Basin in Siberia. Global and Planetary Change, 48(1), 96–111. https://doi.org/10.1016/j.gloplacha.2004.12.007

Liu, J., Chen, J., Xu, J., Lin, Y., Yuan, Z., & Zhou, M. (2019). Attribution of

runoff variation in the headwaters of the Yangtze River based on the

Budyko hypothesis. International Journal of Environmental Research and

Public Health, 16(14), 2506. https://doi.org/10.3390/ijerph16142506

Liu, L., Niu, Q., Heng, J., Li, H., & Xu, Z. (2019). Transition characteristics of

the dry-wet regime and vegetation dynamic responses over the

Yarlung Zangbo River Basin, Southeast Qinghai–Tibet Plateau. Remote

Sensing, 11(10), 1254. https://doi.org/10.3390/rs11101254

Liu, T. (1999). Hydrological characteristics of Yarlung Zangbo River. Acta

Geographica Sinica, S1, 157–164.Liu, W., Wang, L., Zhou, J., Li, Y., Sun, F., Fu, G., Li, X., & Sang, Y. (2016). A

worldwide evaluation of basin-scale evapotranspiration estimates

against the water balance method. Journal of Hydrology, 538, 82–95.https://doi.org/10.1016/j.jhydrol.2016.04.006

Liu, X., Xu, Z., Liu, W., & Liu, L. (2019). Responses of hydrological pro-

cesses to climate change in the Yarlung Zangbo River basin. Hydrologi-

cal Sciences Journal, 64(16), 2057–2067. https://doi.org/10.1080/

02626667.2019.1662908

Liu, Z., Yao, Z., Huang, H., Wu, S., & Liu, G. (2014). Land use and climate

changes and their impacts on runoff in the Yarlung Zangbo River

Basin, China. Land Degradation & Development, 25(3), 203–215.https://doi.org/10.1002/ldr.1159

Lo Vecchio, A., Lenzano, M., Durand, M., Lannutti, E., Bruce, R., &

Lenzano, L. (2018). Estimation of surface flow speed and ice surface

temperature from optical satellite imagery at Viedma glacier, Argen-

tina. Global and Planetary Change, 169, 202–213. https://doi.org/10.1016/j.gloplacha.2018.08.001

Lv, L., & Li, Z. (2013). Variability recognition of runoff in the middle and

lower reaches of Yarlung Zangbo River. Water Power, 39(5), 12–15.Lv, Y., Dong, G., Yang, S., Zhou, Q., & Cai, M. (2014). Spatio-temporal vari-

ation in NDVI in the Yarlung Zangbo River Basin and its relationship

with precipitation and elevation. Resources Science, 36(3), 603–611.Mann, H. B. (1945). Nonparametric tests against trend. Econometrica, 13

(3), 245–259.Matthews, T., & Hodgkins, R. (2016). Interdecadal variability of degree-day

factors on Vestari Hagafellsjökull (Langjökull, Iceland) and the impor-

tance of threshold air temperatures. Journal of Glaciology, 62(232),

310–322. https://doi.org/10.1017/jog.2016.21Mavromatis, T., & Stathis, D. (2011). Response of the water balance in

Greece to temperature and precipitation trends. Theoretical and

Applied Climatology, 104(1), 13–24. https://doi.org/10.1007/s00704-010-0320-9

Milly, P. C. D. (1994). Climate, interseasonal storage of soil water, and the

annual water balance. Advances in Water Resources, 17(1–2), 19–24.https://doi.org/10.1016/0309-1708(94)90020-5

Ning, T., Li, Z., & Liu, W. (2016). Separating the impacts of climate change

and land surface alteration on runoff reduction in the Jing River catch-

ment of China. CATENA, 147, 80–86. https://doi.org/10.1016/j.

catena.2016.06.041

Ohmura, A. (2012). Enhanced temperature variability in high-altitude cli-

mate change. Theoretical and Applied Climatology, 110(4), 499–508.https://doi.org/10.1007/s00704-012-0687-x

Peng, J., Liu, Z., Liu, Y., Wu, J., & Han, Y. (2012). Trend analysis of vegeta-

tion dynamics in Qinghai–Tibet Plateau using Hurst exponent. Ecologi-

cal Indicators, 14(1), 28–39. https://doi.org/10.1016/j.ecolind.2011.

08.011

Pettitt, A. N. (1979). A non-parametric approach to the change-point prob-

lem. Applied Statistics, 28(2), 126–135. https://doi.org/10.2307/

2346729

Ruprecht, J. K., & Schofield, N. J. (1991a). Effects of partial deforestation

on hydrology and salinity in high salt storage landscapes. I. Extensive

block clearing. Journal of Hydrology, 129(1), 19–38. https://doi.org/10.1016/0022-1694(91)90042-G

Ruprecht, J. K., & Schofield, N. J. (1991b). Effects of partial deforestation

on hydrology and salinity in high salt storage landscapes. II. Strip, soils

and parkland clearing. Journal of Hydrology, 129(1), 39–55. https://doi.org/10.1016/0022-1694(91)90043-H

Schaake, J. C. (1990). From climate to flow, in climate change and U.S. In

P. E. Waggoner (Ed.), Water resources (pp. 177–206). John Wiley.

Sen, P. K. (1968). Estimates of the regression coefficient based on

Kendall's tau. Journal of the American Statistical Association, 63(324),

1379–1389. https://doi.org/10.1080/01621459.1968.10480934Sheffield, J., Goteti, G., & Wood, E. F. (2006). Development of a 50-year

high-resolution global dataset of meteorological forcings for land sur-

face modeling. Journal of Climate, 19(13), 3088–3111. https://doi.org/10.1175/JCLI3790.1

Sneyers, R. (1975). Sur l'analyse statistique des séries d'observations. WMO.

St. Jacques, J., & Sauchyn, D. J. (2009). Increasing winter baseflow and

mean annual streamflow from possible permafrost thawing in the

Northwest Territories, Canada. Geophysical Research Letters, 36(1).

L01401. https://doi.org/10.1029/2008GL035822

Su, F., Zhang, L., Ou, T., Chen, D., Yao, T., Tong, K., & Qi, Y. (2016). Hydro-

logical response to future climate changes for the major upstream river

basins in the Tibetan Plateau. Global and Planetary Change, 136,

82–95. https://doi.org/10.1016/j.gloplacha.2015.10.012Sung, J. H., Chung, E., Kim, Y., & Lee, B. (2017). Meteorological hazard

assessment based on trends and abrupt changes in rainfall characteris-

tics on the Korean peninsula. Theoretical and Applied Climatology, 127

(1–2), 305–326. https://doi.org/10.1007/s00704-015-1581-0Tang, L., Zhang, Z., & Wang, X. (2010). Streamflow response to climate

and land use changes in Qingshui River watershed in the loess hilly–gully region of Western Shanxi Province, China. Chinese Journal of

20 of 26 XIN ET AL.

Plant Ecology, 34(7), 800–810. https://doi.org/10.3773/j.issn.1005-

264x.2010.07.005

Tian, L., Yao, T., Numaguti, A., & Duan, K. (2001). Relation between stable

isotope in monsoon precipitation in southern Tibetan Plateau and

moisture transport history. Science in China Series D: Earth Sciences, 44

(1), 267–274. https://doi.org/10.1007/BF02911996Tong, S., Lai, Q., Zhang, J., Bao, Y., Lusi, A., Ma, Q., … Zhang, F. (2018). Spa-

tiotemporal drought variability on the Mongolian Plateau from

1980–2014 based on the SPEI-PM, intensity analysis and Hurst expo-

nent. Science of the Total Environment, 615, 1557–1565. https://doi.org/10.1016/j.scitotenv.2017.09.121

Tuteja, N. K., & Cunnane, C. (1997). Modelling coupled transport of mass

and energy into the snowpack—Model development, validation and

sensitivity analysis. Journal of Hydrology, 195(1), 232–255. https://doi.org/10.1016/S0022-1694(96)03236-2

Wang, D., & Tang, Y. (2014). A one-parameter Budyko model for water

balance captures emergent behavior in Darwinian hydrologic models.

Geophysical Research Letters, 41(13), 4569–4577. https://doi.org/10.1002/2014GL060509

Wang, G., Zhang, J., He, R., Jiang, N., & Jing, X. (2008). Runoff reduction

due to environmental changes in the Sanchuanhe river basin. Interna-

tional Journal of Sediment Research, 23(2), 174–180. https://doi.org/10.1016/S1001-6279(08)60017-7

Wang, S., Zhang, Z., Sun, G., Zhang, M., & Zhang, X. (2006). Effects of land

use change on hydrological dynamics at watershed scale in the Loess

Plateau – A case study in the Luergou watershed, Gansu Province.

Journal of Beijing Forestry University, 1, 48–54.Wang, T., Shi, Y., & Guo, D. (2012). Frozen ground map of China based on a

map of the glaciers, frozen ground and deserts in China (1981–2006).National Tibetan Plateau Data Center. https://doi.org/10.11888/

Geocry.tpdc.270038

Wang, T., Yang, H., Yang, D., Qin, Y., & Wang, Y. (2018). Quantifying the

streamflow response to frozen ground degradation in the source region

of the Yellow River within the Budyko framework. Journal of Hydrology,

558, 301–313. https://doi.org/10.1016/j.jhydrol.2018.01.050Wang, W., Shao, Q., Yang, T., Peng, S., Xing, W., Sun, F., & Luo, Y. (2013).

Quantitative assessment of the impact of climate variability and

human activities on runoff changes: A case study in four catchments

of the Haihe River basin, China. Hydrological Processes, 27(8),

1158–1174. https://doi.org/10.1002/hyp.9299Wang, X. (2015). Study on the spatial and temporal characteristics of

water circulation in the Yalung Zangbo River Basin. Tibet Science and

Technology, 7, 8–12.Wong, H., Hu, B. Q., Ip, W. C., & Xia, J. (2006). Change-point analysis of

hydrological time series using grey relational method. Journal of

Hydrology, 324(1), 323–338. https://doi.org/10.1016/j.jhydrol.2005.

10.007

Wu, J., Miao, C., Wang, Y., Duan, Q., & Zhang, X. (2017). Contribution

analysis of the long-term changes in seasonal runoff on the Loess Pla-

teau, China, using eight Budyko-based methods. Journal of Hydrology,

545, 263–275. https://doi.org/10.1016/j.jhydrol.2016.12.050Wu, Y., Wang, N., He, J., & Jiang, X. (2015). Estimating mountain glacier

surface temperatures from Landsat-ETM + thermal infrared data: A

case study of Qiyi glacier, China. Remote Sensing of Environment, 163,

286–295. https://doi.org/10.1016/j.rse.2015.03.026Xing, S., & Zheng, X. (2003). The coupled numerical model of water and

heat transfer in snow layer. Journal of Taiyuan University of Technology,

6, 647–650.Xiong, D., Yang, Z., Chen, X., & Zhou, H. (2006). Analysis on landscape pat-

tern in the upper and middle reaches of Yarlung Zangbo River: Taking

Zhongba County, Angren County, Rikaze City as example. Wuhan Uni-

versity Journal of Natural Sciences, 11(4), 951–957. https://doi.org/10.1007/BF02830193

Xu, X., Yang, D., Yang, H., & Lei, H. (2014). Attribution analysis based on

the Budyko hypothesis for detecting the dominant cause of runoff

decline in Haihe basin. Journal of Hydrology, 510, 530–540. https://doi.org/10.1016/j.jhydrol.2013.12.052

Xue, B., Wang, L., Li, X., Yang, K., Chen, D., & Sun, L. (2013). Evaluation of

evapotranspiration estimates for two river basins on the Tibetan Pla-

teau by a water balance method. Journal of Hydrology, 492, 290–297.https://doi.org/10.1016/j.jhydrol.2013.04.005

Yang, D., Zhang, S., & Xu, X. (2015). Attribution analysis for runoff decline

in Yellow River Basin during past fifty years based on Budyko hypoth-

esis. Scientia Sinica Technologica, 45(10), 1024–1034.Yang, H., Qi, J., Xu, X., Yang, D., & Lv, H. (2014). The regional variation in

climate elasticity and climate contribution to runoff across China. Jour-

nal of Hydrology, 517, 607–615. https://doi.org/10.1016/j.jhydrol.

2014.05.062

Yang, H., & Yang, D. (2012). Climatic factors influencing changing pan

evaporation across China from 1961 to 2001. Journal of Hydrology,

414–415, 184–193. https://doi.org/10.1016/j.jhydrol.2011.10.043Yang, H., Yang, D., & Hu, Q. (2014). An error analysis of the Budyko

hypothesis for assessing the contribution of climate change to runoff.

Water Resources Research, 50, 9620–9629. https://doi.org/10.1002/2014WR015451

Yang, H., Yang, D., Lei, Z., & Sun, F. (2008). New analytical derivation of

the mean annual water-energy balance equation. Water Resources

Research, 44(3). W03410. https://doi.org/10.1029/2007WR006135

Yao, J., Yang, Q., Mao, W., Zhao, Y., & Xu, X. (2016). Precipitation trend–elevation relationship in arid regions of the China. Global and Planetary

Change, 143, 1–9. https://doi.org/10.1016/j.gloplacha.2016.05.007Yao, T., Li, Z., Yang, W., Guo, X., Zhu, L., Kang, S., Wu, Y. H., & Yu, W.

(2010). Glacial distribution and mass balance in the Yarlung Zangbo

River and its influence on lakes. Chinese Science Bulletin, 55(20),

2072–2078. https://doi.org/10.1007/s11434-010-3213-5Ye, B., Yang, D., Zhang, Z., & Kane, D. L. (2009). Variation of hydrological

regime with permafrost coverage over Lena Basin in Siberia. Journal of

Geophysical Research: Atmospheres, 114(D7). D07102. https://doi.org/

10.1029/2008JD010537

Yin, Y., Liu, H., Yi, X., & Liu, W. (2015). Spatiotemporal variation and abrupt

change analysis of temperature from 1960 to 2012 in the Huang-

Huai-Hai Plain, China. Advances in Meteorology (6), 1–11. https://doi.org/10.1155/2015/643493

Zeng, S., Xia, J., & Du, H. (2014). Separating the effects of climate change

and human activities on runoff over different time scales in the Zhang

River basin. Stochastic Environmental Research and Risk Assessment, 28

(2), 401–413. https://doi.org/10.1007/s00477-013-0760-8Zeng, S., Zhan, C., Sun, F., Du, H., & Wang, F. (2015). Effects of climate

change and human activities on surface runoff in the Luan River basin.

Advances in Meteorology, 2015, 1–12. https://doi.org/10.1155/2015/740239

Zhang, A., Zhang, C., Fu, G., Wang, B., Bao, Z., & Zheng, H. (2012). Assess-

ments of impacts of climate change and human activities on runoff

with SWAT for the Huifa River Basin, Northeast China. Water

Resources Management, 26, 2199–2217. https://doi.org/10.1007/

s11269-012-0010-8

Zhang, C., Shoemaker, C. A., Woodbury, J. D., Cao, M., & Zhu, X. (2013).

Impact of human activities on stream flow in the Biliu River basin,

China. Hydrological Processes, 27(17), 2509–2523. https://doi.org/10.1002/hyp.9389

Zhang, D., Cong, Z., Ni, G., Yang, D., & Hu, S. (2015). Effects of snow ratio

on annual runoff within the Budyko framework. Hydrology and Earth

System Sciences, 19(4), 1977–1992. https://doi.org/10.5194/hess-19-1977-2015

Zhang, L., Dawes, W. R., & Walker, G. R. (2001). Response of mean annual

evapotranspiration to vegetation changes at catchment scale. Water

Resources Research, 37(3), 701–708. https://doi.org/10.1029/

2000WR900325

Zhang, L., Hickel, K., Dawes, W. R., Chiew, F., Western, A. W., &

Briggs, P. R. (2004). A rational function approach for estimating mean

XIN ET AL. 21 of 26

annual evapotranspiration. Water Resources Research, 40(2). W02502.

https://doi.org/10.1029/2003WR002710

Zhang, L., Su, F., Yang, D., Hao, Z., & Tong, K. (2013). Discharge regime

and simulation for the upstream of major rivers over Tibetan Plateau.

Journal of Geophysical Research: Atmospheres, 118(15), 8500–8518.https://doi.org/10.1002/jgrd.50665

Zhang, M., Wei, X., Sun, P., & Liu, S. (2012). The effect of forest harvesting

and climatic variability on runoff in a large watershed: The case study

in the Upper Minjiang River of Yangtze River basin. Journal of Hydrol-

ogy, 464–465, 1–11. https://doi.org/10.1016/j.jhydrol.2012.05.050Zhang, M., Wen, Z., Dong, J., Wang, D., Hou, Y., Wang, B., … Wei, H.

(2019). Mechanism of climate warming on thermal-moisture dynamics

of active permafrost layer considering effect of rainfall. Rock and Soil

Mechanics, 40(5), 1983–1992.Zhang, W., Yi, Y., Song, K., Kimball, J., & Lu, Q. (2016). Hydrological

response of alpine wetlands to climate warming in the Eastern Tibetan

Plateau. Remote Sensing, 8(4), 336. https://doi.org/10.3390/

rs8040336

Zhang, X., Tang, Q., Pan, M., & Tang, Y. (2014). A long-term land surface

hydrologic fluxes and states dataset for China. Journal of Hydrometeo-

rology, 15(5), 2067–2084. https://doi.org/10.1175/JHM-D-13-0170.1

Zhang, X., Zhang, L., Zhao, J., Rustomji, P., & Hairsine, P. (2008). Responses

of streamflow to changes in climate and land use/cover in the Loess

Plateau, China. Water Resources Research, 44(7). W00A07. https://doi.

org/10.1029/2007WR006711

Zhang, Y., Guan, D., Jin, C., Wang, A., Wu, J., & Yuan, F. (2011). Analysis of

impacts of climate variability and human activity on streamflow for a

river basin in Northeast China. Journal of Hydrology, 410(3), 239–247.https://doi.org/10.1016/j.jhydrol.2011.09.023

Zhao, Q., Ding, Y., Wang, J., Gao, H., Zhang, S., Zhao, C., Xu, J., Han, H., &

Shangguan, D. (2019). Projecting climate change impacts on hydrologi-

cal processes on the Tibetan Plateau with model calibration against

the glacier inventory data and observed streamflow. Journal of Hydrol-

ogy, 573, 60–81. https://doi.org/10.1016/j.jhydrol.2019.03.043Zhao, Y., Yang, N., Wei, Y., Hu, B., Cao, Q., Tong, K., & Liang, Y. (2019).

Eight hundred years of drought and flood disasters and precipitation

sequence reconstruction in Wuzhou City, Southwest China. Water, 11

(2). 219. https://doi.org/10.3390/w11020219

Zhao, Z., Fu, Q., Gao, C., Zhang, X., & Xu, Y. (2017). Simulation of monthly

runoff considering flow components in Yarlung Zangbo River. Journal

of China Hydrology, 37(2), 26–30.Zheng, H., Zhang, L., Liu, C., Shao, Q., & Fukushima, Y. (2007). Changes in

stream flow regime in headwater catchments of the Yellow River basin

since the 1950s. Hydrological Processes, 21(7), 886–893. https://doi.org/10.1002/hyp.6280

Zheng, H., Zhang, L., Zhu, M., Zhu, R., Liu, C., Sato, Y., & Fukushima, Y.

(2009). Responses of streamflow to climate and land surface change in

the headwaters of the Yellow River Basin. Water Resources Research,

45. W00A19. https://doi.org/10.1029/2007WR006665

Zuo, D., Xu, Z., Wu, W., Zhao, J., & Zhao, F. (2014). Identification of

streamflow response to climate change and human activities in the

Wei River Basin, China. Water Resources Management, 28(3), 833–851.https://doi.org/10.1007/s11269-014-0519-0

How to cite this article: Xin J, Sun X, Liu L, et al. Quantifying

the contribution of climate and underlying surface changes to

alpine runoff alterations associated with glacier melting.

Hydrological Processes. 2021;35:e14069. https://doi.org/10.

1002/hyp.14069

22 of 26 XIN ET AL.

APPENDIX A.

TABLE A1 Global climate models used as historical forcing data in the study by Su et al. (2016)

Modelling group Institute ID model nameAtmosphere resolution(longitude × latitude in degrees)

Beijing Climate Center, China Meteorological

Administration

BCC BCC-CSM1.1 2.8125 × 2.7906

College of Global Change and Earth System Science,

Beijing Normal University

GCESS BNU-ESM 2.8125 × 2.7906

Canadian Centre for Climate Modeling and Analysis CCCMA CanESM2 2.8125 × 2.7906

National Center for Atmospheric Research NCAR CCSM4 1.2500 × 0.9424

The First Institute of Oceanography, SOA, China FIO FIO-ESM 2.8125 × 2.7906

NOAA Geophysical Fluid Dynamics Laboratory NOAA GFDL GFDL-CM3 2.5000 × 2.0000

GFDL-ESM2G 2.5000 × 2.0225

GFDL-ESM2M 2.5000 × 2.0225

NASA Goddard Institute for Space Studies NASA GISS GISS-E2-R 2.5000 × 2.0000

National Institute of Meteorological Research/Korea

Meteorological Administration

NIMR/KMA HadGEM2-AO 1.8750 × 1.2500

Met Office Hadley Centre MOHC HadGEM2-ES 1.8750 × 1.2500

Institute Pierre-Simon Laplace IPSL IPSL-CM5A-LR 3.7500 × 1.8947

IPSL-CM5A-MR 2.5000 × 1.2676

Japan Agency for Marine-Earth Science and

Technology, Atmosphere and Ocean Research

MIROC MIROC-ESM 2.8125 × 2.7906

Institute (The University of Tokyo), and National

Institute for Environmental Studies

MIROC-ESM-CHEM 2.8125 × 2.7906

Atmosphere and Ocean Research Institute (The

University of Tokyo), National Institute for

Environmental Studies, and Japan Agency for

Marine-Earth Science and Technology

MIROC MIROC5 1.4063 × 1.4008

Max Planck Institute for Meteorology MPI-M MPI-ESM-LR 1.8750 × 1.8653

Meteorological Research Institute MRI MRI-CGCM3 1.1250 × 1.1215

Norwegian Climate Centre NCC NorESM1-M 2.5000 × 1.8947

NorESM1-ME 2.5000 × 1.8947

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TABLE A3 Sensitivity of runoff (Rt) to precipitation (P), potential evapotranspiration (ET0), underlying surface (n), and glacier runoff (r) duringperiod I (baseline period) with different abrupt change point (1995, 1996, and 1997)

Region Abrupt change point εP εET0 εn εr

Upper 1995 1.57 −0.57 −1.47 0.03

1996 1.57 −0.57 −1.48 0.03

1997 1.57 −0.57 −1.48 0.03

Middle 1995 1.33 −0.33 −1.06 0.11

1996 1.33 −0.33 −1.05 0.11

1997 1.33 −0.33 −1.05 0.11

Lower 1995 1.01 −0.01 −0.08 0.15

1996 1.01 −0.01 −0.10 0.15

1997 1.01 −0.01 −0.10 0.15

Note: At the abrupt change point of 1995, period I was from 1966 to 1995; at the abrupt change point of 1996, period I was from 1966 to 1996; at the abrupt

change point of 1997, period I was from 1966 to 1997.

TABLE A4 Sensitivity of runoff (Rt) to precipitation (P), potential evapotranspiration (ET0), underlying surface (n), and glacier runoff (r) duringperiod II (change period) with different abrupt change point (1995, 1996, and 1997)

Region Abrupt change point εP εET0 εn εr

Upper 1995 1.52 −0.52 −1.42 0.13

1996 1.52 −0.52 −1.41 0.13

1997 1.51 −0.51 −1.40 0.13

Middle 1995 1.28 −0.28 −0.92 0.20

1996 1.27 −0.27 −0.91 0.18

1997 1.27 −0.27 −0.91 0.20

Lower 1995 1.02 −0.02 −0.17 0.16

1996 1.02 −0.02 −0.15 0.16

1997 1.02 −0.02 −0.15 0.16

Note: At the abrupt change point of 1995, period II was from 1996 to 2015; at the abrupt change point of 1996, period II was from 1997 to 2015; at the abrupt

change point of 1997, period II was from 1998 to 2015.

TABLE A2 The contribution rate of precipitation (C_(P)), potential evapotranspiration (C_(ET0)) underlying surface (C_(n)), and melting glacier(C_(r)) to the runoff variation with different abrupt change point (1995, 1996, and 1997)

Region Abrupt change point C_(P) C_(ET0) C_(n) C_(r)

Upper 1995 −3.49 −7.36 58.91 58.67

1996 −4.88 −8.89 67.62 53.50

1997 −2.78 −5.30 59.61 49.18

Middle 1995 39.68 −0.68 33.95 27.48

1996 39.48 −0.73 38.44 23.16

1997 39.36 −1.36 36.40 26.04

Lower 1995 203.23 −0.19 −133.31 31.37

1996 143.66 −0.14 −72.48 29.12

1997 129.21 −0.17 −58.74 29.80

24 of 26 XIN ET AL.

F IGURE A1 Comparison results of mean air temperature in the upper (a), middle (b), and lower (c) regions, and the entire basin (d). Temp_PGArepresents the average temperature of the Princeton Global Forcings (PGA) (Sheffield et al., 2006), Temp_CMFD represents the averagetemperature of the China meteorological forcing dataset (CMFD) (He et al., 2020). F represents the value of the F-test, and F > 3.86 represents asignificance level of 0.05

XIN ET AL. 25 of 26

F IGURE A2 Comparison results of mean downward shortwave radiation in the upper (a), middle (b), and lower (c) regions, and the entirebasin (d). Dsrad_PGA represents the downward shortwave radiation of the Princeton Global Forcings (PGA) (Sheffield et al., 2006), Dsrad_CMFDrepresents the downward shortwave radiation of the China meteorological forcing dataset (CMFD) (He et al., 2020). F represents the F-teststatistic, and F > 3.86 represents a significance level of 0.05

26 of 26 XIN ET AL.