Using Median Point in Keeling Plot to Reduce the Uncertainty of the Isotopic Composition of Evapotranspiration

Yusen Yuan aCenter for Agricultural Water Research in China, China Agricultural University, Beijing, China
bDepartment of Earth and Environmental Sciences, Indiana University Indianapolis, Indianapolis, Indiana
cDepartment of Plant and Environmental Sciences, New Mexico State University, Las Cruces, New Mexico
dDepartment of Environmental Sciences, University of California Riverside, California

Search for other papers by Yusen Yuan in
Current site
Google Scholar
PubMed
Close
https://orcid.org/0000-0001-5086-0023
,
Lixin Wang bDepartment of Earth and Environmental Sciences, Indiana University Indianapolis, Indianapolis, Indiana

Search for other papers by Lixin Wang in
Current site
Google Scholar
PubMed
Close
,
Zhongwang Wei eGuangdong Province Key Laboratory for Climate Change and Natural Disaster Studies, School of Atmospheric Sciences, Sun Yat-sen University, Guangzhou, Guangdong, China

Search for other papers by Zhongwang Wei in
Current site
Google Scholar
PubMed
Close
,
Hoori Ajami dDepartment of Environmental Sciences, University of California Riverside, California

Search for other papers by Hoori Ajami in
Current site
Google Scholar
PubMed
Close
,
Honglang Wang fDepartment of Mathematical Sciences, Indiana University Indianapolis, Indianapolis, Indiana

Search for other papers by Honglang Wang in
Current site
Google Scholar
PubMed
Close
, and
Taisheng Du aCenter for Agricultural Water Research in China, China Agricultural University, Beijing, China

Search for other papers by Taisheng Du in
Current site
Google Scholar
PubMed
Close
Free access

Abstract

The isotopic composition of evapotranspiration δET is a crucial parameter in isotope-based evapotranspiration (ET) partitioning and moisture recycling studies. The Keeling plot method is the most prevalent method to calculate δET, though it contains large extrapolated uncertainties from the least squares regression. Traditional Keeling regression uses the mean point of individual measurements. Here, a modified Keeling plot framework was proposed using the median point of individual measurements. We tested the δET uncertainty using the mean point [σET (mean)] and median point [σET (median)]. Multiple resolutions of input and output data from six independent sites were used to test the performance of the two methods. The σET (mean) would be greater than σET (median) when the mean value of inverse vapor concentration (1/Cυ¯) is greater than the median value of inverse vapor concentration [1/Cυ(median)]. When applying the filter of r2 > 0.8, around 70% of σET (mean) was greater than σET (median). This phenomenon might be due to the normality of the vapor concentration Cυ producing the asymmetric distribution of 1/Cυ. The median method could perform significantly better than the mean method when inputting high-resolution measurements (e.g., 1 Hz) and when the water vapor concentration Cυ is relatively low. Compared to the mean method, applying the median method could on average reduce 6.88% of ET partitioning uncertainties and could on average reduce 9.00% of moisture recycling uncertainties. This study provided a new insight of the Keeling plot method and emphasized handling model output uncertainty from multiple perspectives instead of only from input parameters.

© 2024 American Meteorological Society. This published article is licensed under the terms of the default AMS reuse license. For information regarding reuse of this content and general copyright information, consult the AMS Copyright Policy (www.ametsoc.org/PUBSReuseLicenses).

Corresponding authors: Yusen Yuan, yuseny@nmsu.edu; Taisheng Du, dutaisheng@cau.edu

Abstract

The isotopic composition of evapotranspiration δET is a crucial parameter in isotope-based evapotranspiration (ET) partitioning and moisture recycling studies. The Keeling plot method is the most prevalent method to calculate δET, though it contains large extrapolated uncertainties from the least squares regression. Traditional Keeling regression uses the mean point of individual measurements. Here, a modified Keeling plot framework was proposed using the median point of individual measurements. We tested the δET uncertainty using the mean point [σET (mean)] and median point [σET (median)]. Multiple resolutions of input and output data from six independent sites were used to test the performance of the two methods. The σET (mean) would be greater than σET (median) when the mean value of inverse vapor concentration (1/Cυ¯) is greater than the median value of inverse vapor concentration [1/Cυ(median)]. When applying the filter of r2 > 0.8, around 70% of σET (mean) was greater than σET (median). This phenomenon might be due to the normality of the vapor concentration Cυ producing the asymmetric distribution of 1/Cυ. The median method could perform significantly better than the mean method when inputting high-resolution measurements (e.g., 1 Hz) and when the water vapor concentration Cυ is relatively low. Compared to the mean method, applying the median method could on average reduce 6.88% of ET partitioning uncertainties and could on average reduce 9.00% of moisture recycling uncertainties. This study provided a new insight of the Keeling plot method and emphasized handling model output uncertainty from multiple perspectives instead of only from input parameters.

© 2024 American Meteorological Society. This published article is licensed under the terms of the default AMS reuse license. For information regarding reuse of this content and general copyright information, consult the AMS Copyright Policy (www.ametsoc.org/PUBSReuseLicenses).

Corresponding authors: Yusen Yuan, yuseny@nmsu.edu; Taisheng Du, dutaisheng@cau.edu

1. Introduction

As a crucial transport pathway between the land surface and atmosphere (Jung et al. 2010), terrestrial evapotranspiration (ET) is the sum of physically controlled evaporation E and biochemical promoted transpiration T (Scott et al. 2006), as well as an integral input to the free atmosphere (Trenberth 1999). Although ET has become widely accessible through cooperated networks using the eddy covariance approach (Novick et al. 2018), researchers are unable to partition ET only using water vapor fluxes (Scott et al. 2021). The individual measurements of E and T could be a solution for ET partitioning studies, but the disagreements between E + T and ET brought about large uncertainties (Herbst et al. 1996; Li et al. 2010; Singer et al. 2010; Wei et al. 2017). The hydrogen and oxygen isotopes (2H and 18O) have been applied in hydrological studies since the 1960s. With the advent of the high-frequency isotope analyzer (Wang et al. 2009) allowing an output of 1-Hz atmospheric vapor concentration Cυ and its isotopes δυ, each source water could be either measured or simulated with relatively high precision. As such, the isotope method is becoming a powerful method for ET partitioning (Wang et al. 2010; Wei et al. 2018; Xiao et al. 2018), which bypassed the disagreements between E + T and ET.

The isotopic composition of ET (δET) is an important parameter when calculating T of total ET (FT) and moisture recycling using the stable isotope-based method. Although some novel δET algorithms have been developed in recent two decades (Griffis et al. 2010; Lee et al. 2007), the Keeling plot method is the most prevalent one (Keeling 1958; Moreira et al. 1997; Yakir and Wang 1996; Yakir and Sternberg 2000), which occupied 43% of studies reviewed by Rothfuss et al. (2021), as its uncertainty is the same as the gradient method but significantly smaller than the eddy covariance isotopic flux method (Good et al. 2012). However, the δET uncertainty contributed to FT uncertainty was 49%–74% depending on sites (Chen et al. 2022; Cui et al. 2020; Yuan et al. 2022), which is far more than that of the other two parameters, the isotopic composition of evaporation δE and the isotopic composition of evaporation δT. To make it worse, the δET uncertainty contribution would increase with the increase of FT (Chen et al. 2022). As T dominates ET at a global scale (Jasechko et al. 2013; Wang et al. 2014), δET would significantly transfer uncertainty to FT among most terrestrial ecosystems.

Previously, researchers made more efforts to reduce uncertainties on δE and δT reviewed by Xiao et al. (2018), while rarely on δET. After Phillips and Gregg (2001) proposed the first-order Taylor series expansion formula of isotope-based FT uncertainty, researchers attempted to reduce δET uncertainty by using the correlation coefficient r2 filter (Wei et al. 2015), using data from various heights (Griffis et al. 2010), and avoiding averaging initial data (Good et al. 2012). The main challenge to reduce δET uncertainty nowadays is less likely to further optimize the input parameters: the individual measurement of the vapor concentration Cυi and the isotopic composition of water vapor δυi, respectively. The optimizations of the δET derivation algorithms could be a more realistic choice.

In this study, a modified Keeling plot framework was proposed using the median point of individual measurements, whose δET uncertainty would decrease, resulting in a decrease of FT uncertainty. Theoretical derivations were presented and verified by vapor concentration and isotope datasets from six sites with multiple input and output resolutions.

2. Materials and methods

a. Traditional Keeling plot method for δET

From the principle of isotopic mass balance, we have
δυ=SCυ+δET.
With multiple measurements of Cυi and δυi collected at various heights, the traditional Keeling plot framework considered that the intercept I of the ordinary least squares (OLS) regression between 1/Cυi and δυi is δET, and assuming the slope S = CA(δAδET) of this OLS regression is constant. More recently, Yuan et al. (2022) proved that if I = δET and S = CA(δAδET), where CA is the concentration of advection water vapor and δυ and 1/Cυ in Eq. (1) has to be the mean values of 1/Cυi (1/Cυ¯) and the mean values of δυi (δ¯υ), respectively. This is an equivalent condition when applying traditional intercept-based Keeling plot:
δ¯υ=SCυ¯+I.
The traditional Keeling plot uses a linear regression superficially, which is derived by the mean values of vapor concentration and its isotopic composition:
δET(mean)=I=δ¯υSCυ¯.
As a result, the traditional intercept-based δET is the δET generated from the mean values of vapor concentration and its isotopic composition [δET (mean)], replacing δυ in Eq. (1) with δ¯υ in Eq. (3) and replacing 1/Cυ in Eq. (1) with 1/Cυ¯ in Eq. (3). Although the mean values of observation data are considered to be representative, it would be better to use medians to strengthen the robustness against outliers (Hatfield and Prueger 2015).

b. Median method for δET

In this study, a new insight into the δET algorithm was established using the median value of observation data [δET (median)]:
δET(median)=δυ(median)SCυ(median),
where 1/Cυ (median) is equal to the median values of 1/Cυi and δυ (median) is equal to the median values of δυi.

c. The uncertainty of δET (mean) and δET (median)

Following Good et al. (2012) to assume the variance of the individual measurement points (1/Cυi, δυi) is caused by the independent variable δυi, the variance of δET (mean) [σET2(mean)] and the variance of S(σS2) can be shown as the following form (details in the appendix):
σET2(mean)=ψ2[1n+(1Cυ¯)2i=1N(1Cυi1Cυ¯)2],
σS2=ψ21i=1N(1Cυi1Cυ¯)2,
where ψ2=[1/(n2)]i=1n[δυiδET(k/Cυi)]2=[1/(n2)]i=1nRδυi2, and n is the number of the observation points (1/Cυi, δυi). The i=1nRδυi2 is the residual sum of squares of the Keeling plot regression.
In terms of the principle of the univariate linear regression (Montgomery et al. 2021), we have
δυN(I+SCυ,[1n+(1Cυ1Cυ¯)2i=1N(1Cυi1Cυ¯)2]ψ2).
When δυ is δ¯υ, we have δ¯υN[I+(S/C¯υ),ψ2/n] whose variance σ¯υ2 is ψ2/n. When δυ is δυ (median), we have
δυ(median)N(I+SCυ(median),{1n+[1Cυ(median)1Cυ¯]2i=1N(1Cυi1Cv¯)2}ψ2),
whose variance [συ2(median)] is shown as
συ2(median)=ψ2{1n+[1Cυ(median)1Cυ¯]2i=1N(1Cυi1Cυ¯)2}.
According to the error transfer function, the variance of δET (median) [σET2(median)] can be formed as
σET2(median)=συ2(median)+[1Cυ(median)]2σS2=ψ2{1n+[1Cυ(median)1Cυ¯]2+[1Cυ(median)]2i=1N(1Cυi1Cυ¯)2}=ψ2{1n+(1Cυ¯)221Cυ(median)[1Cυ¯1Cυ(median)]i=1N(1Cυi1Cυ¯)2}.
As i=1N[(1/Cυi)(1/Cυ¯)]2=CoV2×(n1)×(1/Cυ¯2), where CoV is the coefficient of variation of 1/Cυi, the variance of δET could be standardized as
σET2(mean)=ψ2[1n+1CoV2(n1)],
σET2(median)=ψ2{1n+12Cυ¯Cυ(median)[1Cυ¯Cυ(median)]CoV2(n1)},
so that the uncertainty of δET (mean) and δET (median) could be
σET(mean)=ψ1n+1CoV2(n1).
σET(median)=ψ1n+12Cυ¯Cυ(median)[1Cυ¯Cυ(median)]CoV2(n1).
Then, the uncertainty reduction Δσ in terms of Eqs. (11) and (12) and the degree of variance reduction (Δσ2/σ2) according to Eqs. (9) and (10) are able to be defined:
Δσ=σET(mean)σET(median)=ψ2Cυ¯Cυ(median)[1Cυ¯Cυ(median)]CoV2(n1),
Δσ2σ2=σET2(mean)σET2(median)σET2(mean)=2Cυ¯Cυ(median)[1Cυ¯Cυ(median)]nCoV2(n1)+n.
As CoV2 is greater than zero, and n ≥ 2, we can conclude that when 1/Cυ¯>1/Cυ(median), σET2(mean)>σET2(median) and σET (mean) σET (median); when 1/Cυ¯<1/Cυ(median), σET2(mean)<σET2(median) and σET (mean) < σET (median). The magnitude of 1/Cυ¯ and 1/Cυ(median) would be the only criteria to determine which method has lower variance and uncertainty. The uncertainty form σ was applied on Δσ to test whether it was over the isotope analyzer precision. The variance form σ2 was applied on Δσ2/σ2 because a more simple relationship between Δσ2/σ2 and 1/Cυ(median) over 1/Cυ¯ would be concluded later in section 4b. Moreover, σ2 was more straightforward to calculate the uncertainty of FT compared to σ. The σ2 is also more widely used in linear regression–related studies (e.g., the Keeling plot regression) than σ (Wiesel et al. 2008).

d. Description of testing datasets

Six sites (Table 1) were selected that contained datasets of Cυ and δυ (both 18O and 2H) to test the performance of the median method. Of these six sites, five of them were from the Stable Water Vapor Isotope Database (SWVID) hosted by Yale University and sponsored by the U.S. National Science Foundation (Wei et al. 2019). The Cυ, δυ, and related meteorology data were stored at hourly resolution in SWVID. Among all 42 sites in SWVID, Heihe (HH), Mase (MS), New Haven (NH), Niwot Ridge (NR), and Rosemount (RM) were selected, which were terrestrial sites, and had been used to simulate δET to make ET partitioning (Berkelhammer et al. 2016; Griffis et al. 2011; Lee et al. 2006; Wei et al. 2015; Wen et al. 2016). The RM site only provided 18O data. The one site outside SWVID was Shiyanghe Experimental Station of China Agricultural University in Wuwei in northwest China. Water isotope measurements have been conducted in the central of a maize field at the Wuwei (WW) site since 2013 (Wu et al. 2018). In situ vapor isotope measurements with the output of 1-Hz Cυ and δυ were installed in the summer of 2017 and 2018 to quantify moisture recycling (Yuan et al. 2020) and FT (Yuan et al. 2022).

Table 1.

List of six sites to verify the median method.

Table 1.

Here, 96 days of data were used in WW, 121 days of data were used in HH, 385 days of data were used in MS, 226 days of data were used in NH, 817 days of data were used in NR, and 61 days of data were used in RM. Each day, Cυi and δυi data from 0700 to 1900 local time were selected to capture the daytime δET. The 1-Hz Cυ and δυ data in WW were aggregated to 1, 5, and 10 min and hourly data by averaging. The daily resolution δET (mean) and δET (median) at six sites using the 1-h resolution input Cυi and δvi data were calculated to test the applicability of the median method among different sites. The performance of the median method with hourly and daily δET output using multiple input resolutions (1 Hz, 1 min, 5 min, 10 min, and 1 h) in WW was also tested. Different criteria r2 of the Keeling plots were considered to evaluate the performance of the median method. As r2 > 0.8 and r2 > 0.6 are the two general criteria to filter the Keeling plots in previous studies (Wei et al. 2015; Yuan et al. 2022), we tested r2 > 0.8, r2 > 0.6, and no filter scenario in this study.

3. Results

a. Comparison between the mean and the median method

The comparisons of δET (mean) and δET (median) among all six sites were performed on both 18O and 2H (Figs. 1a,b). We compared two time resolutions (1 h and daily) of δET calculated by various Cυi and δυi time resolutions (i.e., 1 Hz, 1 min, 5 min, 10 min, and 1 h) in WW and daily δET calculated by hourly Cυi and δυi at the other five sites. The δET (mean) and δET (median) agreed well with each other [δET (median) = 0.9995 δET (mean), R2 = 0.9997*** (where *** indicates statistically significant at p = 0.001)] for both 18O and 2H, which supported the validity of δET (median).

Fig. 1.
Fig. 1.

The comparisons of the isotopic composition of ET based on the mean method [δET (mean)] and the median method [δET (median)] using all six sites for both (a) 18O and (b) 2H. Daily and hourly δET results were not separated in this figure.

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

When using 1-h resolution Cυi and δυi input data and 1-day resolution δET output (Table 2), 27.21% of Keeling plot regression r2 for 18O was greater than 0.8, 44.34% of Keeling plot regression r2 for 18O was greater than 0.6, 17.34% of Keeling plot regression r2 for 2H was greater than 0.8, and 36.86% of Keeling plot regression r2 for 2H was greater than 0.6. The σET2(mean) of 18O was greater than σET2(median) of 18O in 69.63%, 68.87%, and 63.23% cases when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively. The σET2(mean) of 2H was greater than σET2(median) of 2H in 72.22%, 68.65%, and 63.69% cases when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively. Such results suggested that 18O-based Keeling plot regression would have higher r2 than that of 2H, and the δET (median) method might be more useful when r2 was high for both 18O and 2H.

Table 2.

The number of the isotope composition of ET (δET) among six sites in 1-h input resolution and 1-day output resolution when applying various Keeling plot regression r2 filters (>0.8, >0.6, and no filter), and the proportion of the variance of δET using mean point [σET2(mean)] was larger than the variance of δET using median point (median). Both 18O and 2H are listed.

Table 2.

The proportion of the median method better than the mean method in WW (the only site with multiple resolution datasets) with multiple input and output resolution is shown in Table 3. The σET2(mean) was greater than σET2(median) in 81.25% of the cases when δET output was 1-day resolution for both 18O and 2H, while only 49.55% of the cases showed the advantages of the median method when δET output was 1-h resolution for both 18O and 2H. The proportion of the median method better than the mean method significantly decreased with the increased resolution of Cυi and δυi input data, except for 2H at 1-day resolution of δET output. The largest proportion of the median method better than the mean method occurred when using 1-h input and 1-day output, while the lowest proportion of the median method better than the mean method occurred when using 1-Hz input and 1-h output.

Table 3.

The number of the isotope composition of ET (δET) at the WW site using multiple input and output resolutions when applying various Keeling plot regression r2 filters (>0.8, >0.6, and no filter), and the proportion of the variance of δET using mean point [σET2(mean)] was larger than the variance of δET using median point (median). Both 18O and 2H are listed.

Table 3.

b. Uncertainty reduction and variance reduction using the median method

The variance reduction results are shown in Tables 4 and 5, which focus on the cases of σET2(mean)>σET2(median). After applying the median method among six sites, the average uncertainty reduction [Avg(Δσ)] for 18O was 0.10‰, 0.15‰, and 0.29‰ when applying the filters of r2 > 0.8 , r2 > 0.6, and no filters, respectively. The Avg(Δσ) for 2H was 6.60‰, 12.03‰, and 22.90‰ when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively. The precisions of the vapor isotope analyzers (listed in Table 1) were better than 0.20‰ for 18O and 1.00‰ for 2H (Smith et al. 2021; Xu et al. 2022). The Avg(Δσ) would decrease when the stricter r2 filter was applied.

Table 4.

The 18O isotope composition of ET when applying the mean method [σET (mean)(18O)] and the median method [σET (median)(18O)]. The corresponding 18O-based average uncertainty reduction {Avg[Δσ(18O)]}, the average degree of variance reduction {Avg[Δσ2/σ2(18O)]}, and the maximum degree of variance reduction {Max[Δσ2/σ2(18O)]} shown at different sites.

Table 4.
Table 5.

The 2H isotope composition of ET when applying the mean method [σET (mean)(2H)] and the median method [σET (median)(2H)]. The corresponding 2H-based average uncertainty reduction {Avg[Δσ(2H)]}, the average degree of variance reduction {Avg[Δσ2/σ2(2H)]}, and the maximum degree of variance reduction {Max[Δσ2/σ2(2H)]} shown on different sites.

Table 5.

The average variance reduction [Avg(Δσ2/σ2)] for 18O was 9.11%, 7.62%, and 6.40% when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively. Correspondingly, Avg(Δσ2/σ2) for 2H was 9.09%, 7.69%, and 6.30% when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively. The Avg(Δσ2/σ2) would increase with the stricter r2 filter applied. The maximum variance reduction [Max(Δσ2/σ2)] was 33.83% among all six sites.

c. Median method performance using high-resolution input and output data

As is shown in Fig. 2, the overall Avg(Δσ2/σ2) for 18O at WW using 1-day output resolution was 17.12%, 11.54%, and 11.41% when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively, which was higher than that of 1-h output resolution. Similarly, the overall Avg(Δσ2/σ2) for 2H at WW using 1-day input resolution was 15.96%, 10.17%, and 11.41% when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively, which was also higher than that of 1-h output resolution. The overall Avg(Δσ2/σ2) for 18O at WW on 1-Hz input resolution was 16.68%, 12.69%, and 9.63% when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively, which was higher than that of 1-min or 1-h input resolution. Correspondingly, the overall Avg(Δσ2/σ2) for 2H at WW using 1-Hz input resolution was 17.83%, 10.99%, and 9.63% when applying the filters of r2 > 0.8, r2 > 0.6, and no filters, respectively, which was higher than that of 1-min or 1-h input resolution.

Fig. 2.
Fig. 2.

The degree of variance reduction (Δσ2/σ2) among different Keeling plot r2 filters. The input data resolutions are 1 Hz (blank bar), 1 min (line bar), 5 min (cross bar), and 1 h (cross bar), respectively. The output resolutions are 1 day for (a) 18O and (b) 2H and 1 h for (c) 18O and (d) 2H.

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

4. Discussion

a. Why the median method has lower uncertainty and variance than the mean method in most cases

As the magnitude of 1/Cυ¯ and 1/Cυ(median) would be the only criteria to determine which method has lower uncertainty and variance, the proposition of the reason why most time the median method performs better than the mean method is equivalent to the proposition of the reason why in most time 1/Cυ¯>1/Cυ(median).

We noticed that in either traditional Keeling plot algorithm or our median point algorithm, we do not use measured Cυi directly, but we use inversed Cυi. The Cυi normality was tested using the Kolmogorov–Smirnov (K-S) test for 1-Hz, 1-min, and 10-min resolution Cυ data and Shapiro–Wilk (S-W) for 5-min and 1-day resolution Cυ data. Generally, the S-W test is more appropriate for handling sample sizes < 50, whereas the K-S test is used for handling sample sizes > 50. (Mishra et al. 2019; Ruxton et al. 2015). Most (about 75%) Cυi distribution for 1-h input and 1-day output among all six sites were normal distribution (Table 6). As for the various input and output in WW, the rate of σET2(mean)>σET2(median)[R(σET2)] had a proportional relationship with the rate of Cυi distribution passing the normality tests [R(Cυi)] according to Fig. 3 [R(σET2)=2.05×R(Cυi)0.75%, R2 = 0.65]. As a result, the normality of Cυi would lead to 1/Cυ¯>1/Cυ(median), as well as in most cases, the median method had lower uncertainty and variance than the mean method in our study.

Table 6.

The normality test passed rate of the number of the atmosphere vapor concentration Cυ among six sites.

Table 6.
Fig. 3.
Fig. 3.

The rate of the mean method variance greater than the median method variance [R(σET2)] had a proportional relationship with the rate of the individual measurement of vapor concentration distribution that passed the normality tests [R(Cυi)].

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

Theoretically, for a normal distribution AN(μ, σ2), A−1 is an inverse Gaussian (IG) distribution (μ > 0, λ > 0, λ = μ2/σ2) whose skewness 3 × (μ/λ)1/2 is always greater than zero (Chhikara 1988). When the skewness is greater than zero, the mean is greater than the median. Therefore, if CυiN(μ, σ2), 1/Cυi ∼ IG(μ, λ), then 1/Cυ¯>1/Cυ(median). Not only for a normal distribution but also for a uniform distribution AU(a, b), A−1 is a Pareto distribution (xm > 0, α > 3) whose skewness 2(1 + α)/(α − 3) × [(α − 2)/α]1/2 is also always greater than zero (Hosking and Wallis 1987). Therefore, when Cυi is evenly increasing or decreasing to make CυiU(a, b), we still can conclude that 1/Cυ¯>1/Cυ(median).

b. When shall we use the median method for δET?

As is shown in Eq. (14), Δσ2/σ2 is related to CoV2, n, and Cυ¯/Cυ(median). The CoV2 value is extremely small, which had an average value of 7.56 × 10−10 ppm−2 in this study. Thus, CoV2(n − 1) + nn can be applied to simplify Eq. (14) as
Δσ2σ2=σET(mean)2σET(median)2σET(mean)22Cυ¯Cυ(median)[1Cυ¯Cυ(median)],
which was also supported by our in situ data among six sites in Fig. 4. Therefore, the variance reduction is related to the ratio of 1/Cυ(median) over 1/Cυ¯.
Fig. 4.
Fig. 4.

The relationship between the degree of variance reduction (Δσ2/σ2) and the median value of inverse vapor concentration over the mean value of inverse vapor concentration [Cυ (mean)/Cυ (median)].

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

Higher Cυi and δυi input resolution would be the one scenario to make a larger Δσ2/σ2. Inputting 1-Hz data has been shown by Good et al. (2012) that could reduce 94.14% variance for 18O and reduce 95.99% variance for 2H compared with 3-h resolution input data using the traditional Keeling plot method. For a given resolution output δET in this study (Figs. 2a–d), Avg(Δσ2/σ2) would increase with the increase of input Cυi and δυi resolution. The median method would be more useful when the variance of δET had been minimized in the traditional Keeling plot algorithm. One possible reason for this phenomenon is that the kurtoses of Cυi distribution would decrease with the increase of input number (Searls and Intarapanich 1990), which would bring about an increased skewness of its inverse distribution (Figs. 5a,b). Then, 1/Cυ(median) and 1/Cυ¯ would be more separate with an increasing skewness.

Fig. 5.
Fig. 5.

(a) The three illustrated normal distribution (N) density formulas and (b) their corresponding IG distribution density formulas. The dash dot, solid, and short dot lines in (a) represent N (μ = 1, σ2 = 4), N (μ = 1, σ2 = 1), and N (μ = 1, σ2 = 0.25), respectively. The dash dot, solid, and short dot lines in (b) represent IG (μ = 1, λ = 0.25), IG (μ = 1, λ = 1), and IG (μ = 1, λ = 4), respectively, where λ = μ2/σ2.

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

The other scenario to apply the median method would be when Cυ is relatively small. Ideally, when the expectation of Cυi distribution is closer to zero, the variance of 1/Cυi would increase, leading to an increasing distance between 1/Cυ(median) and 1/Cυ¯. Results in our study also proved that relatively high Δσ2/σ2 values occurred when average vapor concentrations were relatively small (Fig. 6). The average Δσ2/σ2 values were higher in WW and HH than those of other four sites, mainly due to WW and HH being in arid areas that have lower Cυ. On 17 May 2012, Δσ2/σ2 value reached its maximum (33.83%) at HH site. When inverse lower Cυi (e.g., 2000 ppm), it would be more likely to be outliers on the Keeling plot regression lines (Figs. 7a,b). ET partitioning has significant importance in quantifying biomass production and understanding the water resource allocation (Kool et al. 2014), especially in arid and semiarid ecosystems (Sun et al. 2019), which occupied 28% of all ET partitioning studies (Rothfuss et al. 2021). The higher Δσ2/σ2 values would significantly reduce the uncertainty of FT calculations in arid and semiarid ecosystems.

Fig. 6.
Fig. 6.

The relationship between the degree of variance reduction (Δσ2/σ2) and the average vapor concentration Cυ.

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

Fig. 7.
Fig. 7.

The Keeling plot regression of (a) 18O and (b) 2H on 17 May 2012 at the HH site, when the degree of variance reduction (Δσ2/σ2) reached the maximum value 33.83%.

Citation: Journal of Hydrometeorology 25, 4; 10.1175/JHM-D-23-0133.1

Although Δσ2/σ2 could be significantly higher when inputting higher resolution Cυi and δυi data, and when Cυ is relatively small, there is an upper bound limit for Δσ2/σ2 when transferring Eq. (15) as follows:
Δσ2σ22Cυ¯Cυ(median)[1Cυ¯Cυ(median)]=2[Cυ¯Cυ(median)12]2+12,
where the maximum Δσ2/σ2 is 0.5 when 1/Cυ¯=2×[1/Cυ(median)].

c. The benefits for ET partitioning and moisture recycling calculations

As δET (mean) and δET (median) were consistent, the ET partitioning results were consistent as well. However, if the median method was applied to obtain δET when 1/Cυ¯>1/Cυ(median), the uncertainty of FT would have decreased. The ET partitioning uncertainty analysis was applied based on the first-order Taylor series approximation (Phillips and Gregg 2001):
σFT=2FT2δETσET2+2FT2δEσE2+2FT2δTσT2,
where σE2 and σT2 represent the variance of δE and δT, respectively, and σFT represents the uncertainty of FT. The σFT usually applies on the daily time scale, as σE2 and σT2 are usually the variance of subdaily δE and δT (Wei et al. 2015; Wu et al. 2018; Xiao et al. 2018). Thus, if σFT is applied at the hourly scale, hourly σE2 and σT2 are zero, and the degree of σFT reduction is σET (median) over σET (mean). Unfortunately, we do not have hourly scale δE and δT data to present hourly σFT results. If daily scale σFT is applied at HH (Wen et al. 2016), MS (Wei et al. 2015), and WW (Yuan et al. 2022), respectively, where δE and δT data are accessible, the daily σFT could on average decrease 0.0061, 0.0016, and 0.0137 in HH, MS, and WW, respectively. That would be 90.56%, 96.34%, and 92.07% of the original daily σFT applied by the mean method (Table 7). If the maximum Δσ2/σ2 is used on each site, the daily σFT could maximally decrease 0.0170, 0.0073, and 0.0244 in HH, MS, and WW, respectively. That would be 82.34%, 85.45%, and 85.86% of the original daily σFT applied by the mean method, respectively. Although the daily σFT decreases, the T/ET results based on the mean method and the median method were both 0.87, 0.89, and 0.80 at HH, MS, and WW, respectively.
Table 7.

The uncertainty of transpiration over evapotranspiration based on the mean method [σFT(mean)] and median method [σFT(median)], respectively. The σFT(mean) and σFT(median) are calculated by the isotope composition of evaporation δE and its uncertainty σE, the isotope composition of transpiration δT and its uncertainty σT, the isotope composition of ET using mean method [δET (mean)] and its uncertainty [σET (mean)], and the isotope composition of ET using median method [δET (median)] and its uncertainty [σET (median)]. Note that δE, δT, σE, and σT are estimated values cited from Wen et al. (2016), Wei et al. (2015), and Yuan et al. (2022), respectively.

Table 7.

Similarly, for local moisture recycling rate calculation, the uncertainty of moisture recycling σMR at a daily time scale could decrease 0.0526 on average at WW (Yuan et al. 2020). That would be 91.00% of the original daily σMR applied by the mean method. Daily σMR could maximally decrease 0.0950 at WW, which would be 83.74% of the original daily σMR applied by the mean method.

d. Implementation of the median method

The traditional Keeling plot inputs 1/Cυ¯, δ¯υ, and s, while the median method inputs 1/Cυ (median), δυ (median), and s. Although σ¯υ2 is always smaller than συ2(median), σET2(mean) is always greater than σET2(median) when 1/Cυ¯>1/Cυ(median) due to the extrapolation algorithm of the Keeling plot. The σET2(mean) would enlarge several times from σ¯υ2 depending on the distance between 1/Cυ¯ and the y axis (Yuan et al. 2022), bringing about a relatively large δET (mean) variance. Using the median method is a compromising strategy to balance the variance of input data and the calculation process. In spite of larger uncertainty in δυ (median) than δ¯υ, the median method finally obtains a lower variance of output δET through a closer extrapolation to the y axis. We cautiously remind researchers to handle model output uncertainty from multiple perspectives rather than only from input parameters.

The traditional Keeling plot method was established by Keeling (Keeling 1958, 1961) to originally capture CO2 emission isotope compositions on a regional basis whose theory is based on the isotope mass balance principle. Apart from water vapor isotopes and 13C isotope from CO2, the Keeling plot has also been explored to intercept the isotope compositions of CH4 fluxes (Fisher et al. 2011) and N2O fluxes (Francis Clar and Anex 2022) to better understand the emission of greenhouse gases. Using the median method in these studies may obtain less variance of the isotope composition of greenhouse gas fluxes. The net ecosystem CO2 exchange consists of soil respiration and gross primary productivity (Gilmanov et al. 2007). The lower variance of the isotope composition of net ecosystem CO2 exchange may lead to less uncertainty of gross primary productivity partitioning.

5. Conclusions

In this study, a novel algorithm was established using the median point of in situ measurements to estimate the isotopic composition of evapotranspiration δET. The theoretical deviation was presented and tested using observation with multiple input and output resolutions from six independent sites. The δET variance σET2 would significantly decrease when the mean value of inverse vapor concentration 1/Cυ¯ was greater than the median value of inverse vapor concentration [1/Cυ(median)]. When applying the filter r2 > 0.8, around 70% of the Keeling plot regression should apply the median method rather than the traditional intercept method as well as the mean method. The criteria of when the median method is better than the mean method are also related to the normality of individual measurement of inverse vapor concentration (1/Cυi). The median method could perform even better when inputting higher time resolution measurement data and when the vapor concentration Cυ is relatively small. When applying the median method at the Wuwei, Heihe, and Mase sites, the average FT uncertainty reduction was 6.88%, and the average moisture recycling uncertainty reduction was 9.00%. This study provided a new insight into the Keeling plot method. The median point theory in this study could be potentially applied to calculate the isotopic composition of CO2, CH4, and N2O using the traditional Keeling plot method.

Acknowledgments.

We acknowledge major support from the National Natural Science Foundation of China (52239002). LW acknowledges partial support from the Department of Energy Grant DE-SC0024297. HA acknowledges partial support from University of California Riverside and the USDA National Institute of Food and Agriculture Hatch funds (PI Ajami CA-R-ENS-5147-H). We thank Dr. Manoj Shukla, Dr. Kenneth Carroll, and Dr. Ray Anderson for your assistance.

Data availability statement.

Data are available at http://vapor-isotope.yale.edu/.

APPENDIX

Variance of Keeling Plot Slope and Intercept

The original form of σET2(mean) and σS2 was proposed by Good et al. (2012):
σET2(mean)=ψ2i=1n1Cυi2n[i=1n1Cυi2(i=1n1Cυi)2n],
σS2=ψ21i=1n1Cυi2(i=1n1Cυi)2n.
Note that i=1n(1/Cυi2){[i=1n(1/Cυi)]2/n}=i=1n[(1/Cυi)(1/Cυ¯)]2 is based on the principle of expectation and variance. As such, Eqs. (A1) and (A2) can be reorganized as
σET2(mean)=ψ2i=1n1Cυi2(i=1n1Cυi)2n+(i=1n1Cυi)2nn[ i=1n1Cυi2(i=1n1Cυi)2n ]=ψ21ni=1n(1Cυi1Cυ¯)2+(1ni=1n1Cυi)2i=1n(1Cυi1Cυ¯)2=ψ2[ 1n+(1Cυ¯)2i=1N(1Cυi1Cυ¯)2 ],
σS2=ψ21i=1N(1Cυi1Cυ¯)2.

REFERENCES

  • Berkelhammer, M., D. C. Noone, T. E. Wong, S. P. Burns, J. F. Knowles, A. Kaushik, P. D. Blanken, and M. W. Williams, 2016: Convergent approaches to determine an ecosystem’s transpiration fraction. Global Biogeochem. Cycles, 30, 933951, https://doi.org/10.1002/2016GB005392.

    • Search Google Scholar
    • Export Citation
  • Chen, H., and Coauthors, 2022: Evapotranspiration partitioning based on field‐stable oxygen isotope observations for an urban locust forest land. Ecohydrology, 15, e2431, https://doi.org/10.1002/eco.2431.

    • Search Google Scholar
    • Export Citation
  • Chhikara, R., 1988: The Inverse Gaussian Distribution: Theory: Methodology, and Applications. Statistics: A Series of Textbooks and Monographs, Vol. 95, CRC Press, 232 pp.

  • Cui, J., L. Tian, Z. Wei, C. Huntingford, P. Wang, Z. Cai, N. Ma, and L. Wang, 2020: Quantifying the controls on evapotranspiration partitioning in the highest alpine meadow ecosystem. Water Resour. Res., 56, e2019WR024815, https://doi.org/10.1029/2019WR024815.

    • Search Google Scholar
    • Export Citation
  • Fisher, R. E., and Coauthors, 2011: Arctic methane sources: Isotopic evidence for atmospheric inputs. Geophys. Res. Lett., 38, L21803, https://doi.org/10.1029/2011GL049319.

    • Search Google Scholar
    • Export Citation
  • Francis Clar, J. T., and R. P. Anex, 2022: Assessing nitrous oxide (N2O) isotopic analyzer performance for in-field use. Agric. For. Meteor., 316, 108855, https://doi.org/10.1016/j.agrformet.2022.108855.

    • Search Google Scholar
    • Export Citation
  • Gilmanov, T. G., and Coauthors, 2007: Partitioning European grassland net ecosystem CO2 exchange into gross primary productivity and ecosystem respiration using light response function analysis. Agric. Ecosyst. Environ., 121, 93120, https://doi.org/10.1016/j.agee.2006.12.008.

    • Search Google Scholar
    • Export Citation
  • Good, S. P., K. Soderberg, L. Wang, and K. K. Caylor, 2012: Uncertainties in the assessment of the isotopic composition of surface fluxes: A direct comparison of techniques using laser‐based water vapor isotope analyzers. J. Geophys. Res., 117, D15301, https://doi.org/10.1029/2011JD017168.

    • Search Google Scholar
    • Export Citation
  • Griffis, T. J., and Coauthors, 2010: Determining the oxygen isotope composition of evapotranspiration using eddy covariance. Bound.-Layer Meteor., 137, 307326, https://doi.org/10.1007/s10546-010-9529-5.

    • Search Google Scholar
    • Export Citation
  • Griffis, T. J., and Coauthors, 2011: Oxygen isotope composition of evapotranspiration and its relation to C4 photosynthetic discrimination. J. Geophys. Res., 116, G01035, https://doi.org/10.1029/2010JG001514.

    • Search Google Scholar
    • Export Citation
  • Hatfield, J. L., and J. H. Prueger, 2015: Temperature extremes: Effect on plant growth and development. Wea. Climate Extremes, 10, 410, https://doi.org/10.1016/j.wace.2015.08.001.

    • Search Google Scholar
    • Export Citation
  • Herbst, M., L. Kappen, F. Thamm, and R. Vanselow, 1996: Simultaneous measurements of transpiration, soil evaporation and total evaporation in a maize field in northern Germany. J. Exp. Bot., 47, 19571962, https://doi.org/10.1093/jxb/47.12.1957.

    • Search Google Scholar
    • Export Citation
  • Hosking, J. R. M., and J. R. Wallis, 1987: Parameter and quantile estimation for the generalized Pareto distribution. Technometrics, 29, 339349, https://doi.org/10.1080/00401706.1987.10488243.

    • Search Google Scholar
    • Export Citation
  • Jasechko, S., Z. D. Sharp, J. J. Gibson, S. J. Birks, Y. Yi, and P. J. Fawcett, 2013: Terrestrial water fluxes dominated by transpiration. Nature, 496, 347350, https://doi.org/10.1038/nature11983.

    • Search Google Scholar
    • Export Citation
  • Jung, M., and Coauthors, 2010: Recent decline in the global land evapotranspiration trend due to limited moisture supply. Nature, 467, 951954, https://doi.org/10.1038/nature09396.

    • Search Google Scholar
    • Export Citation
  • Keeling, C. D., 1958: The concentration and isotopic abundances of atmospheric carbon dioxide in rural areas. Geochim. Cosmochim. Acta, 13, 322334, https://doi.org/10.1016/0016-7037(58)90033-4.

    • Search Google Scholar
    • Export Citation
  • Keeling, C. D., 1961: The concentration and isotopic abundances of carbon dioxide in rural and marine air. Geochim. Cosmochim. Acta, 24, 277298, https://doi.org/10.1016/0016-7037(61)90023-0.

    • Search Google Scholar
    • Export Citation
  • Kool, D., N. Agam, N. Lazarovitch, J. L. Heitman, T. J. Sauer, and A. Ben-Gal, 2014: A review of approaches for evapotranspiration partitioning. Agric. For. Meteor., 184, 5670, https://doi.org/10.1016/j.agrformet.2013.09.003.

    • Search Google Scholar
    • Export Citation
  • Lee, X., R. Smith, and J. Williams, 2006: Water vapour 18O/16O isotope ratio in surface air in New England, USA. Tellus, 58B, 293304, https://doi.org/10.1111/j.1600-0889.2006.00191.x.

    • Search Google Scholar
    • Export Citation
  • Lee, X., K. Kim, and R. Smith, 2007: Temporal variations of the 18O/16O signal of the whole‐canopy transpiration in a temperate forest. Global Biogeochem. Cycles, 21, GB3013, https://doi.org/10.1029/2006GB002871.

    • Search Google Scholar
    • Export Citation
  • Li, X., and Coauthors, 2010: Modeling cherry orchard evapotranspiration based on an improved dual-source model. Agric. Water Manage., 98, 1218, https://doi.org/10.1016/j.agwat.2010.07.019.

    • Search Google Scholar
    • Export Citation
  • Mishra, P., C. M. Pandey, U. Singh, A. Gupta, C. Sahu, and A. Keshri, 2019: Descriptive statistics and normality tests for statistical data. Ann. Card. Anaesth., 22, 6772, https://doi.org/10.4103/aca.ACA_157_18.

    • Search Google Scholar
    • Export Citation
  • Montgomery, D. C., E. A. Peck, and G. G. Vining, 2021: Introduction to Linear Regression Analysis. John Wiley and Sons, 704 pp.

  • Moreira, M., L. Sternberg, L. Martinelli, R. Victoria, E. Barbosa, L. Bonates, and D. Nepstad, 1997: Contribution of transpiration to forest ambient vapour based on isotopic measurements. Global Change Biol., 3, 439450, https://doi.org/10.1046/j.1365-2486.1997.00082.x.

    • Search Google Scholar
    • Export Citation
  • Novick, K. A., J. A. Biederman, A. R. Desai, M. E. Litvak, D. J. P. Moore, R. L. Scott, and M. S. Torn, 2018: The AmeriFlux network: A coalition of the willing. Agric. For. Meteor., 249, 444456, https://doi.org/10.1016/j.agrformet.2017.10.009.

    • Search Google Scholar
    • Export Citation
  • Phillips, D. L., and J. W. Gregg, 2001: Uncertainty in source partitioning using stable isotopes. Oecologia, 127, 171179, https://doi.org/10.1007/s004420000578.

    • Search Google Scholar
    • Export Citation
  • Rothfuss, Y., M. Quade, N. Brüggemann, A. Graf, H. Vereecken, and M. Dubbert, 2021: Reviews and syntheses: Gaining insights into evapotranspiration partitioning with novel isotopic monitoring methods. Biogeosciences, 18, 37013732, https://doi.org/10.5194/bg-18-3701-2021.

    • Search Google Scholar
    • Export Citation
  • Ruxton, G. D., D. M. Wilkinson, and M. Neuhäuser, 2015: Advice on testing the null hypothesis that a sample is drawn from a normal distribution. Anim. Behav., 107, 249252, https://doi.org/10.1016/j.anbehav.2015.07.006.

    • Search Google Scholar
    • Export Citation
  • Scott, R. L., T. E. Huxman, W. L. Cable, and W. E. Emmerich, 2006: Partitioning of evapotranspiration and its relation to carbon dioxide exchange in a Chihuahuan Desert shrubland. Hydrol. Processes, 20, 32273243, https://doi.org/10.1002/hyp.6329.

    • Search Google Scholar
    • Export Citation
  • Scott, R. L., J. F. Knowles, J. A. Nelson, P. Gentine, X. Li, G. Barron-Gafford, R. Bryant, and J. A. Biederman, 2021: Water availability impacts on evapotranspiration partitioning. Agric. For. Meteor., 297, 108251, https://doi.org/10.1016/j.agrformet.2020.108251.

    • Search Google Scholar
    • Export Citation
  • Searls, D. T., and P. Intarapanich, 1990: A note on an estimator for the variance that utilizes the kurtosis. Amer. Stat., 44, 295296.

    • Search Google Scholar
    • Export Citation
  • Singer, J. W., J. L. Heitman, G. Hernandez-Ramirez, T. J. Sauer, J. H. Prueger, and J. L. Hatfield, 2010: Contrasting methods for estimating evapotranspiration in soybean. Agric. Water Manage., 98, 157163, https://doi.org/10.1016/j.agwat.2010.08.014.

    • Search Google Scholar
    • Export Citation
  • Smith, D. F., M. T. Moore, R. L. Anderson, and A. E. Carey, 2021: Hydrological separation of event and pre-event soil water in a cultivated landscape. ACS Agric. Sci. Technol., 2, 3241, https://doi.org/10.1021/acsagscitech.1c00088.

    • Search Google Scholar
    • Export Citation
  • Sun, X., B. P. Wilcox, and C. B. Zou, 2019: Evapotranspiration partitioning in dryland ecosystems: A global meta-analysis of in situ studies. J. Hydrol., 576, 123136, https://doi.org/10.1016/j.jhydrol.2019.06.022.

    • Search Google Scholar
    • Export Citation
  • Trenberth, K. E., 1999: Atmospheric moisture recycling: Role of advection and local evaporation. J. Climate, 12, 13681381, https://doi.org/10.1175/1520-0442(1999)012<1368:AMRROA>2.0.CO;2.

    • Search Google Scholar
    • Export Citation
  • Wang, L., K. K. Caylor, and D. Dragoni, 2009: On the calibration of continuous, high‐precision δ18O and δ2H measurements using an off‐axis integrated cavity output spectrometer. Rapid Commun. Mass Spectrom., 23, 530536, https://doi.org/10.1002/rcm.3905.

    • Search Google Scholar
    • Export Citation
  • Wang, L., K. K. Caylor, J. C. Villegas, G. A. Barron‐Gafford, D. D. Breshears, and T. E. Huxman, 2010: Partitioning evapotranspiration across gradients of woody plant cover: Assessment of a stable isotope technique. Geophys. Res. Lett., 37, L09401, https://doi.org/10.1029/2010GL043228.

    • Search Google Scholar
    • Export Citation
  • Wang, L., S. P. Good, and K. K. Caylor, 2014: Global synthesis of vegetation control on evapotranspiration partitioning. Geophys. Res. Lett., 41, 67536757, https://doi.org/10.1002/2014GL061439.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., K. Yoshimura, A. Okazaki, W. Kim, Z. Liu, and M. Yokoi, 2015: Partitioning of evapotranspiration using high‐frequency water vapor isotopic measurement over a rice paddy field. Water Resour. Res., 51, 37163729, https://doi.org/10.1002/2014WR016737.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., K. Yoshimura, L. Wang, D. G. Miralles, S. Jasechko, and X. Lee, 2017: Revisiting the contribution of transpiration to global terrestrial evapotranspiration. Geophys. Res. Lett., 44, 27922801, https://doi.org/10.1002/2016GL072235.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., X. Lee, X. Wen, and W. Xiao, 2018: Evapotranspiration partitioning for three agro-ecosystems with contrasting moisture conditions: A comparison of an isotope method and a two-source model calculation. Agric. For. Meteor., 252, 296310, https://doi.org/10.1016/j.agrformet.2018.01.019.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., and Coauthors, 2019: A global database of water vapor isotopes measured with high temporal resolution infrared laser spectroscopy. Sci. Data, 6, 180302, https://doi.org/10.1038/sdata.2018.302.

    • Search Google Scholar
    • Export Citation
  • Wen, X., B. Yang, X. Sun, and X. Lee, 2016: Evapotranspiration partitioning through in-situ oxygen isotope measurements in an oasis cropland. Agric. For. Meteor., 230231, 8996, https://doi.org/10.1016/j.agrformet.2015.12.003.

    • Search Google Scholar
    • Export Citation
  • Wiesel, A., Y. C. Eldar, and A. Yeredor, 2008: Linear regression with Gaussian model uncertainty: Algorithms and bounds. IEEE Trans. Signal Process., 56, 21942205, https://doi.org/10.1109/TSP.2007.914323.

    • Search Google Scholar
    • Export Citation
  • Wu, Y., T. Du, Y. Yuan, and M. K. Shukla, 2018: Stable isotope measurements show increases in corn water use efficiency under deficit irrigation. Sci. Rep., 8, 14113, https://doi.org/10.1038/s41598-018-32368-4.

    • Search Google Scholar
    • Export Citation
  • Xiao, W., Z. Wei, and X. Wen, 2018: Evapotranspiration partitioning at the ecosystem scale using the stable isotope method—A review. Agric. For. Meteor., 263, 346361, https://doi.org/10.1016/j.agrformet.2018.09.005.

    • Search Google Scholar
    • Export Citation
  • Xu, T., H. Pang, Z. Zhan, W. Zhang, H. Guo, S. Wu, and S. Hou, 2022: Water vapor isotopes indicating rapid shift among multiple moisture sources for the 2018–2019 winter extreme precipitation events in southeastern China. Hydrol. Earth Syst. Sci., 26, 117127, https://doi.org/10.5194/hess-26-117-2022.

    • Search Google Scholar
    • Export Citation
  • Yakir, D., and X.-F. Wang, 1996: Fluxes of CO2 and water between terrestrial vegetation and the atmosphere estimated from isotope measurements. Nature, 380, 515517, https://doi.org/10.1038/380515a0.

    • Search Google Scholar
    • Export Citation
  • Yakir, D., and L. D. S. L. Sternberg, 2000: The use of stable isotopes to study ecosystem gas exchange. Oecologia, 123, 297311, https://doi.org/10.1007/s004420051016.

    • Search Google Scholar
    • Export Citation
  • Yuan, Y., T. Du, H. Wang, and L. Wang, 2020: Novel Keeling-plot-based methods to estimate the isotopic composition of ambient water vapor. Hydrol. Earth Syst. Sci., 24, 44914501, https://doi.org/10.5194/hess-24-4491-2020.

    • Search Google Scholar
    • Export Citation
  • Yuan, Y., L. Wang, H. Wang, W. Lin, W. Jiao, and T. Du, 2022: A modified isotope-based method for potential high-frequency evapotranspiration partitioning. Adv. Water Resour., 160, 104103, https://doi.org/10.1016/j.advwatres.2021.104103.

    • Search Google Scholar
    • Export Citation
Save
  • Berkelhammer, M., D. C. Noone, T. E. Wong, S. P. Burns, J. F. Knowles, A. Kaushik, P. D. Blanken, and M. W. Williams, 2016: Convergent approaches to determine an ecosystem’s transpiration fraction. Global Biogeochem. Cycles, 30, 933951, https://doi.org/10.1002/2016GB005392.

    • Search Google Scholar
    • Export Citation
  • Chen, H., and Coauthors, 2022: Evapotranspiration partitioning based on field‐stable oxygen isotope observations for an urban locust forest land. Ecohydrology, 15, e2431, https://doi.org/10.1002/eco.2431.

    • Search Google Scholar
    • Export Citation
  • Chhikara, R., 1988: The Inverse Gaussian Distribution: Theory: Methodology, and Applications. Statistics: A Series of Textbooks and Monographs, Vol. 95, CRC Press, 232 pp.

  • Cui, J., L. Tian, Z. Wei, C. Huntingford, P. Wang, Z. Cai, N. Ma, and L. Wang, 2020: Quantifying the controls on evapotranspiration partitioning in the highest alpine meadow ecosystem. Water Resour. Res., 56, e2019WR024815, https://doi.org/10.1029/2019WR024815.

    • Search Google Scholar
    • Export Citation
  • Fisher, R. E., and Coauthors, 2011: Arctic methane sources: Isotopic evidence for atmospheric inputs. Geophys. Res. Lett., 38, L21803, https://doi.org/10.1029/2011GL049319.

    • Search Google Scholar
    • Export Citation
  • Francis Clar, J. T., and R. P. Anex, 2022: Assessing nitrous oxide (N2O) isotopic analyzer performance for in-field use. Agric. For. Meteor., 316, 108855, https://doi.org/10.1016/j.agrformet.2022.108855.

    • Search Google Scholar
    • Export Citation
  • Gilmanov, T. G., and Coauthors, 2007: Partitioning European grassland net ecosystem CO2 exchange into gross primary productivity and ecosystem respiration using light response function analysis. Agric. Ecosyst. Environ., 121, 93120, https://doi.org/10.1016/j.agee.2006.12.008.

    • Search Google Scholar
    • Export Citation
  • Good, S. P., K. Soderberg, L. Wang, and K. K. Caylor, 2012: Uncertainties in the assessment of the isotopic composition of surface fluxes: A direct comparison of techniques using laser‐based water vapor isotope analyzers. J. Geophys. Res., 117, D15301, https://doi.org/10.1029/2011JD017168.

    • Search Google Scholar
    • Export Citation
  • Griffis, T. J., and Coauthors, 2010: Determining the oxygen isotope composition of evapotranspiration using eddy covariance. Bound.-Layer Meteor., 137, 307326, https://doi.org/10.1007/s10546-010-9529-5.

    • Search Google Scholar
    • Export Citation
  • Griffis, T. J., and Coauthors, 2011: Oxygen isotope composition of evapotranspiration and its relation to C4 photosynthetic discrimination. J. Geophys. Res., 116, G01035, https://doi.org/10.1029/2010JG001514.

    • Search Google Scholar
    • Export Citation
  • Hatfield, J. L., and J. H. Prueger, 2015: Temperature extremes: Effect on plant growth and development. Wea. Climate Extremes, 10, 410, https://doi.org/10.1016/j.wace.2015.08.001.

    • Search Google Scholar
    • Export Citation
  • Herbst, M., L. Kappen, F. Thamm, and R. Vanselow, 1996: Simultaneous measurements of transpiration, soil evaporation and total evaporation in a maize field in northern Germany. J. Exp. Bot., 47, 19571962, https://doi.org/10.1093/jxb/47.12.1957.

    • Search Google Scholar
    • Export Citation
  • Hosking, J. R. M., and J. R. Wallis, 1987: Parameter and quantile estimation for the generalized Pareto distribution. Technometrics, 29, 339349, https://doi.org/10.1080/00401706.1987.10488243.

    • Search Google Scholar
    • Export Citation
  • Jasechko, S., Z. D. Sharp, J. J. Gibson, S. J. Birks, Y. Yi, and P. J. Fawcett, 2013: Terrestrial water fluxes dominated by transpiration. Nature, 496, 347350, https://doi.org/10.1038/nature11983.

    • Search Google Scholar
    • Export Citation
  • Jung, M., and Coauthors, 2010: Recent decline in the global land evapotranspiration trend due to limited moisture supply. Nature, 467, 951954, https://doi.org/10.1038/nature09396.

    • Search Google Scholar
    • Export Citation
  • Keeling, C. D., 1958: The concentration and isotopic abundances of atmospheric carbon dioxide in rural areas. Geochim. Cosmochim. Acta, 13, 322334, https://doi.org/10.1016/0016-7037(58)90033-4.

    • Search Google Scholar
    • Export Citation
  • Keeling, C. D., 1961: The concentration and isotopic abundances of carbon dioxide in rural and marine air. Geochim. Cosmochim. Acta, 24, 277298, https://doi.org/10.1016/0016-7037(61)90023-0.

    • Search Google Scholar
    • Export Citation
  • Kool, D., N. Agam, N. Lazarovitch, J. L. Heitman, T. J. Sauer, and A. Ben-Gal, 2014: A review of approaches for evapotranspiration partitioning. Agric. For. Meteor., 184, 5670, https://doi.org/10.1016/j.agrformet.2013.09.003.

    • Search Google Scholar
    • Export Citation
  • Lee, X., R. Smith, and J. Williams, 2006: Water vapour 18O/16O isotope ratio in surface air in New England, USA. Tellus, 58B, 293304, https://doi.org/10.1111/j.1600-0889.2006.00191.x.

    • Search Google Scholar
    • Export Citation
  • Lee, X., K. Kim, and R. Smith, 2007: Temporal variations of the 18O/16O signal of the whole‐canopy transpiration in a temperate forest. Global Biogeochem. Cycles, 21, GB3013, https://doi.org/10.1029/2006GB002871.

    • Search Google Scholar
    • Export Citation
  • Li, X., and Coauthors, 2010: Modeling cherry orchard evapotranspiration based on an improved dual-source model. Agric. Water Manage., 98, 1218, https://doi.org/10.1016/j.agwat.2010.07.019.

    • Search Google Scholar
    • Export Citation
  • Mishra, P., C. M. Pandey, U. Singh, A. Gupta, C. Sahu, and A. Keshri, 2019: Descriptive statistics and normality tests for statistical data. Ann. Card. Anaesth., 22, 6772, https://doi.org/10.4103/aca.ACA_157_18.

    • Search Google Scholar
    • Export Citation
  • Montgomery, D. C., E. A. Peck, and G. G. Vining, 2021: Introduction to Linear Regression Analysis. John Wiley and Sons, 704 pp.

  • Moreira, M., L. Sternberg, L. Martinelli, R. Victoria, E. Barbosa, L. Bonates, and D. Nepstad, 1997: Contribution of transpiration to forest ambient vapour based on isotopic measurements. Global Change Biol., 3, 439450, https://doi.org/10.1046/j.1365-2486.1997.00082.x.

    • Search Google Scholar
    • Export Citation
  • Novick, K. A., J. A. Biederman, A. R. Desai, M. E. Litvak, D. J. P. Moore, R. L. Scott, and M. S. Torn, 2018: The AmeriFlux network: A coalition of the willing. Agric. For. Meteor., 249, 444456, https://doi.org/10.1016/j.agrformet.2017.10.009.

    • Search Google Scholar
    • Export Citation
  • Phillips, D. L., and J. W. Gregg, 2001: Uncertainty in source partitioning using stable isotopes. Oecologia, 127, 171179, https://doi.org/10.1007/s004420000578.

    • Search Google Scholar
    • Export Citation
  • Rothfuss, Y., M. Quade, N. Brüggemann, A. Graf, H. Vereecken, and M. Dubbert, 2021: Reviews and syntheses: Gaining insights into evapotranspiration partitioning with novel isotopic monitoring methods. Biogeosciences, 18, 37013732, https://doi.org/10.5194/bg-18-3701-2021.

    • Search Google Scholar
    • Export Citation
  • Ruxton, G. D., D. M. Wilkinson, and M. Neuhäuser, 2015: Advice on testing the null hypothesis that a sample is drawn from a normal distribution. Anim. Behav., 107, 249252, https://doi.org/10.1016/j.anbehav.2015.07.006.

    • Search Google Scholar
    • Export Citation
  • Scott, R. L., T. E. Huxman, W. L. Cable, and W. E. Emmerich, 2006: Partitioning of evapotranspiration and its relation to carbon dioxide exchange in a Chihuahuan Desert shrubland. Hydrol. Processes, 20, 32273243, https://doi.org/10.1002/hyp.6329.

    • Search Google Scholar
    • Export Citation
  • Scott, R. L., J. F. Knowles, J. A. Nelson, P. Gentine, X. Li, G. Barron-Gafford, R. Bryant, and J. A. Biederman, 2021: Water availability impacts on evapotranspiration partitioning. Agric. For. Meteor., 297, 108251, https://doi.org/10.1016/j.agrformet.2020.108251.

    • Search Google Scholar
    • Export Citation
  • Searls, D. T., and P. Intarapanich, 1990: A note on an estimator for the variance that utilizes the kurtosis. Amer. Stat., 44, 295296.

    • Search Google Scholar
    • Export Citation
  • Singer, J. W., J. L. Heitman, G. Hernandez-Ramirez, T. J. Sauer, J. H. Prueger, and J. L. Hatfield, 2010: Contrasting methods for estimating evapotranspiration in soybean. Agric. Water Manage., 98, 157163, https://doi.org/10.1016/j.agwat.2010.08.014.

    • Search Google Scholar
    • Export Citation
  • Smith, D. F., M. T. Moore, R. L. Anderson, and A. E. Carey, 2021: Hydrological separation of event and pre-event soil water in a cultivated landscape. ACS Agric. Sci. Technol., 2, 3241, https://doi.org/10.1021/acsagscitech.1c00088.

    • Search Google Scholar
    • Export Citation
  • Sun, X., B. P. Wilcox, and C. B. Zou, 2019: Evapotranspiration partitioning in dryland ecosystems: A global meta-analysis of in situ studies. J. Hydrol., 576, 123136, https://doi.org/10.1016/j.jhydrol.2019.06.022.

    • Search Google Scholar
    • Export Citation
  • Trenberth, K. E., 1999: Atmospheric moisture recycling: Role of advection and local evaporation. J. Climate, 12, 13681381, https://doi.org/10.1175/1520-0442(1999)012<1368:AMRROA>2.0.CO;2.

    • Search Google Scholar
    • Export Citation
  • Wang, L., K. K. Caylor, and D. Dragoni, 2009: On the calibration of continuous, high‐precision δ18O and δ2H measurements using an off‐axis integrated cavity output spectrometer. Rapid Commun. Mass Spectrom., 23, 530536, https://doi.org/10.1002/rcm.3905.

    • Search Google Scholar
    • Export Citation
  • Wang, L., K. K. Caylor, J. C. Villegas, G. A. Barron‐Gafford, D. D. Breshears, and T. E. Huxman, 2010: Partitioning evapotranspiration across gradients of woody plant cover: Assessment of a stable isotope technique. Geophys. Res. Lett., 37, L09401, https://doi.org/10.1029/2010GL043228.

    • Search Google Scholar
    • Export Citation
  • Wang, L., S. P. Good, and K. K. Caylor, 2014: Global synthesis of vegetation control on evapotranspiration partitioning. Geophys. Res. Lett., 41, 67536757, https://doi.org/10.1002/2014GL061439.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., K. Yoshimura, A. Okazaki, W. Kim, Z. Liu, and M. Yokoi, 2015: Partitioning of evapotranspiration using high‐frequency water vapor isotopic measurement over a rice paddy field. Water Resour. Res., 51, 37163729, https://doi.org/10.1002/2014WR016737.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., K. Yoshimura, L. Wang, D. G. Miralles, S. Jasechko, and X. Lee, 2017: Revisiting the contribution of transpiration to global terrestrial evapotranspiration. Geophys. Res. Lett., 44, 27922801, https://doi.org/10.1002/2016GL072235.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., X. Lee, X. Wen, and W. Xiao, 2018: Evapotranspiration partitioning for three agro-ecosystems with contrasting moisture conditions: A comparison of an isotope method and a two-source model calculation. Agric. For. Meteor., 252, 296310, https://doi.org/10.1016/j.agrformet.2018.01.019.

    • Search Google Scholar
    • Export Citation
  • Wei, Z., and Coauthors, 2019: A global database of water vapor isotopes measured with high temporal resolution infrared laser spectroscopy. Sci. Data, 6, 180302, https://doi.org/10.1038/sdata.2018.302.

    • Search Google Scholar
    • Export Citation
  • Wen, X., B. Yang, X. Sun, and X. Lee, 2016: Evapotranspiration partitioning through in-situ oxygen isotope measurements in an oasis cropland. Agric. For. Meteor., 230231, 8996, https://doi.org/10.1016/j.agrformet.2015.12.003.

    • Search Google Scholar
    • Export Citation
  • Wiesel, A., Y. C. Eldar, and A. Yeredor, 2008: Linear regression with Gaussian model uncertainty: Algorithms and bounds. IEEE Trans. Signal Process., 56, 21942205, https://doi.org/10.1109/TSP.2007.914323.

    • Search Google Scholar
    • Export Citation
  • Wu, Y., T. Du, Y. Yuan, and M. K. Shukla, 2018: Stable isotope measurements show increases in corn water use efficiency under deficit irrigation. Sci. Rep., 8, 14113, https://doi.org/10.1038/s41598-018-32368-4.

    • Search Google Scholar
    • Export Citation
  • Xiao, W., Z. Wei, and X. Wen, 2018: Evapotranspiration partitioning at the ecosystem scale using the stable isotope method—A review. Agric. For. Meteor., 263, 346361, https://doi.org/10.1016/j.agrformet.2018.09.005.

    • Search Google Scholar
    • Export Citation
  • Xu, T., H. Pang, Z. Zhan, W. Zhang, H. Guo, S. Wu, and S. Hou, 2022: Water vapor isotopes indicating rapid shift among multiple moisture sources for the 2018–2019 winter extreme precipitation events in southeastern China. Hydrol. Earth Syst. Sci., 26, 117127, https://doi.org/10.5194/hess-26-117-2022.

    • Search Google Scholar
    • Export Citation
  • Yakir, D., and X.-F. Wang, 1996: Fluxes of CO2 and water between terrestrial vegetation and the atmosphere estimated from isotope measurements. Nature, 380, 515517, https://doi.org/10.1038/380515a0.

    • Search Google Scholar
    • Export Citation
  • Yakir, D., and L. D. S. L. Sternberg, 2000: The use of stable isotopes to study ecosystem gas exchange. Oecologia, 123, 297311, https://doi.org/10.1007/s004420051016.

    • Search Google Scholar
    • Export Citation
  • Yuan, Y., T. Du, H. Wang, and L. Wang, 2020: Novel Keeling-plot-based methods to estimate the isotopic composition of ambient water vapor. Hydrol. Earth Syst. Sci., 24, 44914501, https://doi.org/10.5194/hess-24-4491-2020.

    • Search Google Scholar
    • Export Citation
  • Yuan, Y., L. Wang, H. Wang, W. Lin, W. Jiao, and T. Du, 2022: A modified isotope-based method for potential high-frequency evapotranspiration partitioning. Adv. Water Resour., 160, 104103, https://doi.org/10.1016/j.advwatres.2021.104103.

    • Search Google Scholar
    • Export Citation
  • Fig. 1.

    The comparisons of the isotopic composition of ET based on the mean method [δET (mean)] and the median method [δET (median)] using all six sites for both (a) 18O and (b) 2H. Daily and hourly δET results were not separated in this figure.

  • Fig. 2.

    The degree of variance reduction (Δσ2/σ2) among different Keeling plot r2 filters. The input data resolutions are 1 Hz (blank bar), 1 min (line bar), 5 min (cross bar), and 1 h (cross bar), respectively. The output resolutions are 1 day for (a) 18O and (b) 2H and 1 h for (c) 18O and (d) 2H.

  • Fig. 3.

    The rate of the mean method variance greater than the median method variance [R(σET2)] had a proportional relationship with the rate of the individual measurement of vapor concentration distribution that passed the normality tests [R(Cυi)].

  • Fig. 4.

    The relationship between the degree of variance reduction (Δσ2/σ2) and the median value of inverse vapor concentration over the mean value of inverse vapor concentration [Cυ (mean)/Cυ (median)].

  • Fig. 5.

    (a) The three illustrated normal distribution (N) density formulas and (b) their corresponding IG distribution density formulas. The dash dot, solid, and short dot lines in (a) represent N (μ = 1, σ2 = 4), N (μ = 1, σ2 = 1), and N (μ = 1, σ2 = 0.25), respectively. The dash dot, solid, and short dot lines in (b) represent IG (μ = 1, λ = 0.25), IG (μ = 1, λ = 1), and IG (μ = 1, λ = 4), respectively, where λ = μ2/σ2.

  • Fig. 6.

    The relationship between the degree of variance reduction (Δσ2/σ2) and the average vapor concentration Cυ.

  • Fig. 7.

    The Keeling plot regression of (a) 18O and (b) 2H on 17 May 2012 at the HH site, when the degree of variance reduction (Δσ2/σ2) reached the maximum value 33.83%.

All Time Past Year Past 30 Days
Abstract Views 1799 1481 0
Full Text Views 718 650 49
PDF Downloads 219 144 12