Abstract

Abstract. Isotopic labeling techniques have the potential to minimize the uncertainty of plant root water uptake (RWU) profiles estimated using multisource (statistical) modeling by artificially enhancing the soil water isotopic gradient. On the other end of the modeling continuum, physical models can account for hydrodynamic constraints to RWU if simultaneous soil and plant water status data are available. In this study, a population of tall fescue (Festuca arundinacea cv. Soni) was grown in amacro-rhizotron and monitored for a 34 h long period following the oxygen stable isotopic (18O) labeling of deep soil water. Aboveground variables included tiller and leaf water oxygen isotopic compositions (δtiller and δleaf, respectively) as well as leaf water potential (ψleaf), relative humidity, and transpiration rate. Belowground profiles of root length density (RLD), soil water content, and isotopic composition were also sampled. While there were strong correlations between hydraulic variables as well as between isotopic variables, the experimental results underlined the partial disconnect between the temporal dynamics of hydraulic and isotopic variables. In order to dissect the problem, we reproduced both types of observations with a one-dimensional physical model of water flow in the soil–plant domain for 60 different realistic RLD profiles. While simulated ψleaf followed clear temporal variations with small differences across plants, as if they were “onboard the same roller coaster”, simulated δtiller values within the plant population were rather heterogeneous (“swarm-like”) with relatively little temporal variation and a strong sensitivity to rooting depth. Thus, the physical model explained the discrepancy between isotopic and hydraulic observations: the variability captured by δtiller reflected the spatial heterogeneity in the rooting depth in the soil region influenced by the labeling and may not correlate with the temporal dynamics of ψleaf. In other words, ψleaf varied in time with transpiration rate, while δtiller varied across plants with rooting depth. For comparison purposes, a Bayesian statistical model was also used to simulate RWU. While it predicted relatively similar cumulative RWU profiles, the physical model could differentiate the spatial from the temporal dynamics of the isotopic composition. An important difference between the two types of RWU models was the ability of the physical model to simulate the occurrence of hydraulic lift in order to explain concomitant increases in the soil water content and the isotopic composition observed overnight above the soil labeling region.

Highlights

  • Since the seminal work of Washburn and Smith (1934) where it was first reported that willow trees did not fractionate hydrogen stable isotopes in a hydroponic water solution during root water uptake (RWU), water stable isotopologues (1H2H16O and 1H128O) have been used as indicators for plant water sources in soils

  • Light could be shed on RWU of Festuca arundinacea by manipulating the lower boundary conditions for water content and oxygen isotopic composition

  • The new version of the one-dimensional model of Couvreur et al (2014) implemented here accounted for both root and soil hydraulics in a population of “big” root systems of known root length density profile. This approach underlined the high sensitivity of δtiller to rooting depth and suggested that if δtiller is measured on a limited number of individuals, its variations in time may reflect the heterogeneity of the rooting depth within the population rather than temporal dynamics, which was minor in our simulations

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Summary

Introduction

Since the seminal work of Washburn and Smith (1934) where it was first reported that willow trees did not fractionate hydrogen stable isotopes in a hydroponic water solution during root water uptake (RWU), water stable isotopologues (1H2H16O and 1H128O) have been used as indicators for plant water sources in soils. Results only show reasonable precision when (i) the soil water isotopic composition depth gradient is strong and monotonic (which avoids issues of identifiability) and (ii) the temporal dynamics of RWU and the soil water isotopic composition are relatively low. Condition (i) is mostly fulfilled at the surface of the soil, whereas the soil water isotopic composition gradients usually become lower or nonexistent with increasing depth (due to the isotopic influence of the groundwater table and increasing dispersion with depth). Condition (ii) is often neglected, but it is required due to the instantaneous nature of the sap flow samples

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