Elsevier

Agricultural Water Management

Volume 127, September 2013, Pages 85-96
Agricultural Water Management

Partitioning evapotranspiration into soil evaporation and transpiration using a modified dual crop coefficient model in irrigated maize field with ground-mulching

https://doi.org/10.1016/j.agwat.2013.05.018Get rights and content

Highlights

  • We reported a modified dual crop coefficient (Kc) model to partition evapotranspiration.

  • Daily basal Kc was dynamically calculated by introducing canopy cover coefficient.

  • Leaf senescence factor was taken into consideration to modify basal Kc.

  • Evaporation coefficient was modified by accounting for effect of ground-mulching.

  • The good agreements were found through comparing measurements with predictions.

Abstract

The accurate partitioning of crop evapotranspiration (ETc) into two components, soil evaporation (Es) and transpiration (Tr), is needed to better understand terrestrial hydrological cycles and develop precise irrigation scheduling. However, there is no easy way to distinguish between the two. Based on FAO-56 dual crop coefficient (Kc) approach, we developed a modified dual Kc model for better predicting Tr through basal crop coefficient (Kcb) and Es through evaporation coefficient (Ke). Daily Kcb was dynamically calculated by introducing a canopy cover coefficient that could be simply described as a function of leaf area index or fraction of canopy cover. Also, leaf senescence factor was taken into consideration to modify Kcb when leaf suffers functional senescence. Ke was modified through introducing the fraction of ground-mulching (fm) to account for the effect of mulching on Es. The model was parameterized by measurements in 2009, and validated using independent data for grain and seed maize with and without mulching in 2010 and 2011. The results indicate that the predicted Kc values by the modified model were obviously better than those by the original model. The good agreements were found between the predicted ETc, Tr and Es using the modified model and the measurements for grain maize in 2010 with fm = 0.6, with the slope of linear regression of 0.99 (R2 = 0.90), 1.01 (R2 = 0.92) and 0.96 (R2 = 0.78), respectively. The modified model also well reproduced the values of ETc and Es for seed maize in 2011, which had lower plant height and leaf area index compared to grain maize, under mulching (fm = 0.7) and non-mulching (fm = 0) conditions. The slopes of linear regression between predictions and measurements were 0.98 (R2 = 0.91) and 0.99 (R2 = 0.92) for ETc, and 0.98 (R2 = 0.79) and 0.97 (R2 = 0.80) for Es under fm = 0.7 and 0.0, respectively. These results suggest that the modified dual Kc model can accurately predict ETc, Es and Tr for different crop types under different mulching, thus could be a useful tool for improving irrigation water management.

Introduction

Crop evapotranspiration (ETc) plays a key role in energy and water balance of agricultural systems, and is also a key process in the terrestrial hydrological cycle (Burba and Verma, 2005, Zhang et al., 2011a). More than 90% of water used in agriculture is lost by soil evaporation (Es) and crop transpiration (Tr), referring to as ETc (Rana and Katerji, 2000). Transpiration is strongly linked to crop productivity since it occurs simultaneously with photosynthesis through the stomatal pores of leaves (Pieruschka et al., 2010). Conversely, direct soil evaporation is not a contributing factor to crop production, and should be reduced by management practices (e.g., proper irrigation strategies and ground-mulching) (Allen, 2000, Zhao et al., 2010). Whereas the two separate processes of Tr and Es occur simultaneously, and there is no easy way to distinguish between the two (Er-Raki et al., 2010). Therefore, accurate partitioning between soil evaporation and transpiration by models is needed to better understand terrestrial hydrological cycles, develop precise irrigation scheduling, improve crop productivity and enhance water use efficiency.

Several models have been developed to separately predict soil evaporation and transpiration since direct measurement of them is difficult, costly and not available in many regions (Allen et al., 1998, Monteith and Unsworth, 2008, Shuttleworth, 2007, Utset et al., 2004). The direct models include both the single-layer Penman–Monteith and two-layer Shuttleworth–Wallace (Monteith and Unsworth, 2008, Shuttleworth and Wallace, 1985). Many input parameters of these models cannot be easily obtained, thus wide application of these models is limited (Allen, 2000). In addition, weather data are routinely measured only above a grassed surface, so the application of the direct models is limited since the differences may exist between the characteristics of the weather measurements and the feedback that should be presented to reflect ETc of the surface in question (Jarvis and McNaughton, 1986). In contrast, the indirect FAO-56 crop coefficient (Kc) approach has overcome these deficiencies since Kc has contained all differences between the reference surface and the physiologies, physics and morphologies of crop in question (Allen, 2000, Allen et al., 1998). Especially, the dual Kc model has been a preferred approach due to its simplicity for fewer input data and robustness for separately predicting Es and Tr (Allen, 2000, Er-Raki et al., 2010). The dual Kc model has been widely used in scheduling irrigation and improving agricultural production (Allen, 2000, Liu and Luo, 2010, Paço et al., 2011, Zhao and Ji, 2010).

The basal crop coefficient, Kcb, is generally obtained from the guideline of FAO-56 by looking-up the tabulated value at every growth stage and then linearly interpolated to obtain daily values. The approach from the original FAO-56 dual Kc procedures cannot calculate daily actual value of Kcb, although daily actual value is of great importance for accurately calculating the dynamic of Tr. Furthermore, leaf senescence and the decline of physiological function at the late season stage could induce stomatal closure and sharp decrease of Tr (Ding et al., 2013, Steduto and Hsiao, 1998). The original dual Kc model has not taken into consideration the effect of leaf senescence. Thus, it is essential to modify the original dual Kc approach to accomplish daily dynamic calculation of Kcb. Maize, including grain and seed maize, is one of the main crops in arid regions of northwest China, and its water requirement is mainly supplied by irrigation because of low precipitation (Ding et al., 2010, Zhao et al., 2010). To reduce Es, ground is often mulched with plastic film, which is a well-established management strategy and widely used (Ding et al., 2013, Hou et al., 2010, Zhou et al., 2009). Whereas evaporation coefficient (Ke) in FAO-56 was obtained by available energy and soil moisture regimes at the topsoil layer, the effect of ground-mulching on Es was not accounted in Ke. As we have known, Es would definitely decrease when ground is mulched, because the evaporation area is reduced by ground-mulching. The previous studies have indicated that Es was reduced by ∼50% with plastic film mulching over the whole growing season, especially during the early growing stages where soil surface was not fully covered by crop canopy (Hou et al., 2010, Mukherjee et al., 2010, Zhou et al., 2009). At present, an analytical formula of Ke incorporating the effect of mulching on Es in dual Kc model has not been established yet.

In this study, to better partition evapotranspiration into soil evaporation and crop transpiration, a modified dual Kc model was developed through accomplishing daily dynamic estimation of Kcb, and incorporating the effects of leaf senescence and ground-mulching on Tr and Es. Its performance was tested through comparing the predicted ETc, Tr and Es with measurements in irrigated grain and seed maize with and without mulching in northwest China.

Section snippets

The modified dual crop coefficient model

In FAO-56, the actual ETc is defined as the product of crop coefficient (Kc) and reference evapotranspiration (ETo) (Allen et al., 1998).ETc=KcETo

In the dual Kc model, Kc is split into two factors that separately describe the evaporation (Ke) and transpiration (Kcb) components.Kc=KsKcb+Kewhere Ks is water stress coefficient whose value is dependent on available soil water in the root zone. The corresponding crop transpiration (Tr) and soil evaporation (Es) are calculated as follows:Tr=KsKcbEToEs

Study area and experimental arrangement

The experiments were conducted at Shiyanghe Experimental Station for Water-saving in Agriculture and Ecology of China Agricultural University, located in Gansu Province of northwest China (N 37°52′, E 102°50′, altitude 1581 m) during 2009–2010. The site has long sunlight hours with a mean annual sunshine duration over 3000 h, mean annual temperature of 8 °C and frost-free days of 150 d. The region is limited in water resources with a mean annual precipitation of 164 mm and a mean annual pan

Model parameterization and calibration

The water depletion fractions for non-stress conditions (p) were obtained through inverse methods based on 2009 data (Table 2). The initial p value was set as 0.5 during the whole growing period. The iteration terminal criterion was set as less than 5% differences between the measured and predicted Kc averages at every growing stage. The p decreased from 0.55 at the initial stage to 0.45 at the mid-season stage (Table 2). The higher value of p at the initial stage was attributed to lower

Conclusions

The original FAO-56 dual crop coefficient model was modified through introducing a canopy cover coefficient (Kcc), leaf senescence factor (fs), and fraction of ground-mulching (fm). The dynamical basal crop coefficient (Kcb) for predicting transpiration (Tr) was calculated using Kcc. Also, the effect of fs on reduction of Tr was incorporated in Kcb. After accounting for the effect of fm on soil evaporation (Es), evaporation coefficient (Ke) for predicting Es was modified. Observed crop

Acknowledgments

We are grateful to the research grants from the National High-Tech Research and Development Program (2011AA100502, 2013AA102904, and 2013AA103004), the Chinese National Natural Science Fund (51222905 and 91225301), and the Special Fund for Water-scientific Research in the Public Interest, Ministry of Water Resources (201201003). The research is also supported by Chinese Universities Scientific Fund (2013XJ018 and 2013QJ042). The authors also acknowledge the two anonymous reviewers for their

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