**Research article**
13 Aug 2018

**Research article** | 13 Aug 2018

# Multi-source data assimilation for physically based hydrological modeling of an experimental hillslope

Anna Botto, Enrica Belluco, and Matteo Camporese

**Anna Botto et al.**Anna Botto, Enrica Belluco, and Matteo Camporese

- Department of Civil, Environmental and Architectural Engineering, University of Padua, Padua, Italy

- Department of Civil, Environmental and Architectural Engineering, University of Padua, Padua, Italy

**Correspondence**: Anna Botto (anna.botto@unipd.it)

**Correspondence**: Anna Botto (anna.botto@unipd.it)

Received: 18 Jan 2018 – Discussion started: 31 Jan 2018 – Revised: 25 May 2018 – Accepted: 24 Jul 2018 – Published: 13 Aug 2018

Data assimilation has recently been the focus of much attention for integrated surface–subsurface hydrological models, whereby joint assimilation of water table, soil moisture, and river discharge measurements with the ensemble Kalman filter (EnKF) has been extensively applied. Although the EnKF has been specifically developed to deal with nonlinear models, integrated hydrological models based on the Richards equation still represent a challenge, due to strong nonlinearities that may significantly affect the filter performance. Thus, more studies are needed to investigate the capabilities of the EnKF to correct the system state and identify parameters in cases where the unsaturated zone dynamics are dominant, as well as to quantify possible tradeoffs associated with assimilation of multi-source data. Here, the CATHY (CATchment HYdrology) model is applied to reproduce the hydrological dynamics observed in an experimental two-layered hillslope, equipped with tensiometers, water content reflectometer probes, and tipping bucket flow gages to monitor the hillslope response to a series of artificial rainfall events. Pressure head, soil moisture, and subsurface outflow are assimilated with the EnKF in a number of scenarios and the challenges and issues arising from the assimilation of multi-source data in this real-world test case are discussed. Our results demonstrate that the EnKF is able to effectively correct states and parameters even in a real application characterized by strong nonlinearities. However, multi-source data assimilation may lead to significant tradeoffs: the assimilation of additional variables can lead to degradation of model predictions for other variables that are otherwise well reproduced. Furthermore, we show that integrated observations such as outflow discharge cannot compensate for the lack of well-distributed data in heterogeneous hillslopes.

Data assimilation, i.e., the process in which observations of a system are merged in a consistent manner with numerical model predictions (Moradkhani, 2008; Troch et al., 2003), has become increasingly popular in hydrological modeling over the last few decades (Montzka et al., 2012). Among the various techniques available, the ensemble Kalman filter (EnKF) (Evensen, 2003, 2009b) is probably the most widespread, thanks to its ease of implementation, capability to handle nonlinear models and potential to be used as a sequential inverse modeling tool when parameters are included in the update step. Applications in hydrology include studies in different disciplines, such as groundwater hydrology (Bailey and Baù, 2010; Chen and Zhang, 2006; Hendricks Franssen and Kinzelbach, 2008; Li et al., 2012; Zovi et al., 2017), rainfall–runoff modeling (Clark et al., 2008; Han and Li, 2008; Moradkhani et al., 2005; Vrugt et al., 2006; Weerts and El Serafy, 2006; Xie and Zhang, 2010), and land surface modeling at multiple scales (Cammalleri and Ciraolo, 2012; Crow and Wood, 2003; De Lannoy et al., 2007; Flores et al., 2012; Francois et al., 2003; Hain et al., 2012; Pan and Wood, 2006; Reichle et al., 2002a, b).

As a consequence of such popularity, the EnKF is also increasingly applied with integrated surface–subsurface hydrological models (IHSSMs), whereby multiple terrestrial compartments (e.g., snow cover, surface water, groundwater) are solved simultaneously, in an attempt to tackle environmental problems in a holistic approach (Kollet et al., 2017; Maxwell et al., 2014). For instance, Camporese et al. (2009a) and Camporese et al. (2009b) combined the CATHY model and the EnKF to assimilate pressure head, soil moisture, and streamflow data, finding that the assimilation of pressure head and soil moisture is beneficial to subsurface states and river discharge, but the assimilation of river discharge alone does not improve the prediction of subsurface states. Similar conclusions were drawn by Pasetto et al. (2012), who compared the EnKF with a modified particle filter to assimilate discharge and pressure head, using the CATHY model. More recently, Pasetto et al. (2015) used the EnKF and CATHY to investigate the impact of possible sensor failure on the observability of flow dynamics and estimation of the model parameters characterizing the soil properties of an artificial hillslope. Ridler et al. (2014) assimilated soil moisture remote sensing products in the MIKE SHE model and found that surface soil moisture has correction capabilities limited to the first 25 cm of soil. With the same model, Rasmussen et al. (2016), Rasmussen et al. (2015), Zhang et al. (2015), and Zhang et al. (2016) investigated in detail issues related to uncertainty quantification and biased observations, as well the impacts of update localization and ensemble size on the multivariate assimilation of groundwater head and river discharge at the catchment scale. Kurtz et al. (2015) first presented a data assimilation framework for the land surface–subsurface part of the Terrestrial System Modelling Platform (TerrSysMP), followed by Baatz et al. (2017), who assimilated distributed river discharge data into the TerrSysMP to estimate the spatially distributed Manning roughness coefficient, and Zhang et al. (2018), who tested and compared five data assimilation methodologies for assimilating groundwater level data via the EnKF to improve root zone soil moisture estimation. Within yet another modeling framework, Tang et al. (2017) used the EnKF in conjunction with HydroGeoSphere to study the influence of heterogeneous riverbeds on river–aquifer exchange fluxes.

In spite of such a strong interest, several issues related to the use of EnKF for state and parameter estimation in integrated hydrological modeling remain unresolved. The subsurface component of many IHSSMs is based on the solution of the Richards equation in one or three dimensions and, although recent studies with numerical experiments in synthetic test cases (Brandhorst et al., 2017; Erdal et al., 2014) have shown that the EnKF has great potential for the estimation of soil hydraulic parameters in the unsaturated zone, it is still unclear whether the method is able to cope with nonlinearities and parameter estimation in real test cases, where multiple uncertainties on initial and boundary conditions make the problem much more challenging (Bauser et al., 2016; De Lannoy et al., 2007; Monsivais-Huertero et al., 2010; Shi et al., 2015; Visser et al., 2006). Also, as more sources of data become available at cheaper cost, it is increasingly difficult to assess which data types are the most suitable or effective in assimilating and checking which possible tradeoffs might occur when assimilating different variables in a multivariate data assimilation framework. Zhang et al. (2018), for instance, found that joint assimilation of pressure head and soil moisture is beneficial only when pressure head is assimilated in the saturated zone and soil moisture in the unsaturated zone, while Zhang et al. (2016) showed that joint assimilation of groundwater head and water content fails to provide reasonable results if proper countermeasures to spurious correlations are not adopted.

Within this context, the main goals of the present study are (i) to assess whether the EnKF in combination with a Richards equation-based hydrological model is able to effectively improve states and parameters in a real-world test case characterized by dominant unsaturated dynamics and (ii) to quantify the tradeoffs associated with multi-source data assimilation.

To pursue these goals, the EnKF is used in combination with the CATHY (CATchment HYdrology) model (Camporese et al., 2010) to assimilate real observations of pressure head, soil moisture and subsurface outflow collected during a controlled experiment carried out in an artificial hillslope. The experiment is characterized by strong nonlinearities, due to the dominant unsaturated dynamics, but the strictly controlled conditions, as opposed to field studies, allow us to minimize the effects of initial and boundary condition uncertainty. The behavior and performance of the EnKF-based assimilation framework in terms of its ability to retrieve the correct hillslope response are evaluated in a number of data assimilation scenarios, characterized by different combinations of assimilated and updated variables. In each scenario, a significant part of the simulation is devoted to the validation of the model (i.e., with no data assimilation), to assess the impacts of parameter updating on the model predictions, also during periods without observations.

The artificial hillslope is placed inside a concrete structure of length
6 m, width 2 m and height varying linearly from 3.5 to 0.5 m,
corresponding to a slope of 32^{∘} (Fig. 1). A total of
50 apertures, which can be kept closed with screw cups when needed, allow the
positioning of various monitoring sensors in properly chosen positions on
each lateral wall of the structure. The hillslope toe is made with a
hollow-brick porous wall, in order to allow subsurface water to drain. The
soil is placed inside the structure to mimic a two-layered hillslope. A
uniform 60 cm thick silty fine sand is deployed on top of a low-permeable
basement made of sandy clay soil. More details on the soil properties can be
found in Lora et al. (2016a) and Schenato et al. (2017). In the following,
we will refer to the two soil types simply as sand and clay.

Six tensiometers and six water content reflectometer (WCR) probes are used to
measure pressure head and water content in the top soil layer. All the
sensors are located in an intermediate position of the hillslope, as shown in
Fig. 1, which reports a plan view and longitudinal cross
section along with the six positions where each tensiometer has been
installed in front of the corresponding WCR. Two tipping-bucket flow gages
are placed at the toe of the hillslope to measure surface runoff and
subsurface outflow, while the rain is generated by a rainfall simulator that
can produce relatively uniform rainfall intensities varying from 50 to
150 mm h^{−1} (Lora et al., 2016a).

A Campbell Scientific (CR 1000) data logger is used to collect and record all
the data with a frequency of 0.5 Hz during a 12-day experiment, carried
out by generating rainfall events of different duration alternated with
recession periods (no rainfall, evaporation only). Before the experiment, two
preliminary tests were performed to check the intensity and the uniformity of
the rainfall rate. The coefficients of uniformity of the preliminary tests
are equal to 72 %, for a mean rate of 58.8 mm h^{−1}
(Lora et al., 2016a). The
evaporation rate has been measured throughout the experiment by an
atmometer. The average
measured rate is quite small (<1 mm day^{−1}),
consistent with weather and period of the year (November 2016).

Figure 2 reports all the data collected during the experiment. Note that the tensiometers P1 and P4 were affected by malfunctioning; therefore, their data are not reported and were not used in the data assimilation simulations.

## 3.1 The CATHY model

The CATHY model (Camporese et al., 2010) is a physics-based hydrological model capable of simulating integrated subsurface, overland and channel water flow. The model combines a Richards equation solver for the three-dimensional flow in variably saturated porous media with a surface water flow module for the solution of the one-dimensional diffusion wave approximation of the de Saint-Venant equation. In this study, however, there is no surface runoff. Therefore, only subsurface flow is considered, according to the following form of the Richards equation:

In Eq. (1), ${S}_{\mathrm{w}}=\mathit{\theta}/\mathit{\varphi}$ is water saturation,
*θ* and *ϕ* being the volumetric soil water content and porosity
(∕), respectively, *S*_{s} is the specific storage coefficient
(*L*^{−1}), *ψ* is the pressure head (*L*), *t* is time (*T*), ∇ is
the gradient operator, *K*_{s} is the saturated hydraulic conductivity
tensor (*L*∕*T*), *K*_{r} is the relative hydraulic conductivity
function (∕), ${\mathit{\eta}}_{z}=(\mathrm{0},\mathrm{0},\mathrm{1}{)}^{T}$ is the vertical direction
vector, *z* is the vertical coordinate
directed upward (*L*), and *q*_{s} represents distributed source or
sink terms (*L*^{3}∕*L*^{3}*T*).

The unsaturated hydraulic properties are taken into account by means of the
van Genuchten functions (e.g., Wösten and van Genuchten, 1988)
*S*_{w}(*ψ*) and *K*_{r}(*ψ*):

where ${S}_{\mathrm{wr}}={\mathit{\theta}}_{\mathrm{r}}/\mathit{\varphi}$ is the residual water
saturation, with *θ*_{r} the residual water content, *α* is
an empirical constant (*L*^{−1}) related to the inverse of the air entry
suction, and the dimensionless shape parameters *n* and *m* are linked by the
expression $m=\mathrm{1}-\mathrm{1}/n$. The model solves Eq. (1) by means of
Galerkin finite elements with tetrahedral elements and linear basis functions
in space and weighted finite differences for integration in
time (Camporese et al., 2010).

It is worth noting that the Richards equation is strongly nonlinear, due to the retention curves (Eqs. 2 and 3). Such nonlinearities are enhanced in this study by the fact that the hillslope is characterized by dominant unsaturated conditions (Fig. 2), as opposed to many other previous applications of data assimilation with physics-based models. This makes our hillslope experiment particularly challenging and distinctive from both modeling and data assimilation perspectives.

## 3.2 The ensemble Kalman filter

The ensemble Kalman filter (Evensen, 2003, 2009a, b) is a sequential data assimilation scheme, in which states (and parameters) are sequentially updated based on a Monte Carlo approximation of the covariance matrices needed in the standard Kalman filter. The process is Markovian of the first order and the implementation of the EnKF does not require the linearization of the model, making it particularly suitable for handling nonlinear problems.

In this paper the EnKF is implemented according to the numerical formulation
proposed by Sakov et al. (2010). Let **X** be an ensemble matrix of *M*
rows and *N* columns, where *N* is the number of realizations and *M* is the
state dimension, i.e., the number of nodes in the finite element grid,
augmented by the number of parameters that are subject to update. The main
idea behind this type of implementation is that the matrix **X** can
be defined as the sum, **x**+**A**, of the ensemble average,
**x**,

and the matrix of ensemble anomalies, **A**,

where **1** and **I** are a vector with all elements equal to
one and the identity matrix, respectively. As usual, superscript *T* denotes
matrix transposition.

Whenever observed data are available, the EnKF can compute the updated matrix
**X**^{u} as the sum of the updated ensemble mean,
**x**^{u}, and the updated anomalies, **A**^{u}:

In the following, the lack of a superscript u denotes that the matrix or vector is computed at the forecast stage, i.e., at the previous model time step.

The updated mean can be calculated as

where ** β** is a diagonal matrix of dampening factors
(Hendricks Franssen and Kinzelbach, 2008), whose elements vary from 0 to 1, and

**is the scaled innovation vector**

*s*
which depends on the measurement error covariance matrix, **R**, the
difference between the measurements, **D**, and the ensemble mean of
the simulated observations, **Hx**. Dampening factors help to prevent the occurrence
of unstable updates and filter divergence (e.g., Evensen, 2009b) and
were chosen as an alternative to covariance inflation due to ease of
implementation.

The matrix **G** is defined as

where **S** is the matrix of scaled ensemble innovation anomalies

**HA** being the simulated measurement anomalies

and **M** being defined as

The updated anomalies, **A**^{u}, are computed as

When updating the states only, the elements of **X** are the pressure
heads at each node of the finite element grid, while the state augmentation
technique is used when also updating the parameters. In this latter case, the
desired parameters (e.g., hydraulic conductivity, parameters of the retention
curves), transformed as described in Sect. 4.2, are added to
**X** and updated based on their correlation with the system states
(Erdal et al., 2015).

^{a} Rainfall (positive) and evaporation (negative) rates.
^{b} *σ*_{VG} as described in Sect. 4.2.

## 4.1 CATHY setup

The artificial hillslope is discretized with a surface triangular grid resulting from the subdivision of square cells of 10 cm side. The triangular grid is then replicated vertically for a total of 25 layers to generate the three-dimensional tetrahedral mesh (Fig. 3). Fifteen layers are used to represent the top sand, while 10 layers discretize the clay. No flow boundary conditions are assumed at each boundary, except for the subsurface outflow section, where seepage face boundary conditions are used, and the surface, where time-variable rainfall or evaporation rates are imposed. Finally, the soil hydraulic parameters are assigned as reported in Table 1. The values of saturated hydraulic conductivity and van Genuchten retention parameters are perturbed to generate the ensemble of realizations as described in the following section, whereas soil porosities and specific storages are considered deterministic, the former being well characterized with laboratory tests and the latter having little impact on the CATHY model response in this case.

## 4.2 EnKF setup

In order to generate the ensemble of realizations needed for the application of the EnKF, we perturb the atmospheric forcing (i.e., rainfall and evaporation rates), soil properties and initial conditions. Table 1 reports a summary of the perturbed variables, along with their nominal mean values as well as the nature and statistics of the perturbations. The uncertainties on model parameters and boundary conditions have been assigned on the basis of previous modeling experiences and preliminary characterization of the soils in the hillslope (Camporese et al., 2009a, b; Lora et al., 2016b).

The ensemble of time-variable atmospheric forcing rates was generated with a
sequence of multiplicative perturbations, **q**_{k}, correlated in
time as in Evensen (2003):

where the subscript *k* is the time index, **w**_{k} is a sequence
of white noise drawn from the standard normal distribution, and the
coefficient *γ* is computed as

Δ*t* being the assimilation interval and *τ* the specified time
decorrelation length, here set equal to 108 000 s, i.e., 30 h.

The initial conditions consist of a uniform value of pressure head,
*ψ*_{0}, whose nominal ensemble mean is −0.67 m, based on the average
provided by the tensiometer measurements. We opted for a uniform value of
initial pressure head because, at the beginning of the experiment, the entire
hillslope was in a highly unsaturated condition, as derived from the
tensiometer data. This means that, even without an initially hydrostatic
(i.e., equilibrium) profile, water is basically prevented from flowing in or
out of the hillslope due to the very small values of relative hydraulic
conductivity. This is one of the peculiarities of our test case compared to
similar studies. Preliminary analyses showed that the model is not very
sensitive to *ψ*_{0}, because in any case the initial hydraulic
conductivity is so small that the hillslope responds only when the first
rainfall event occurs and starts wetting the soil. Therefore, in this study,
no warm-up or spin-up was necessary. The ensemble of *ψ*_{0} values is
generated by additive perturbations normally distributed with mean equal to 0
and standard deviation equal to 0.2 m.

Perturbed soil parameters, for both sand and clay, include the saturated
hydraulic conductivity as well as the parameters of the van Genuchten
retention curves. Table 1 reports the nominal mean values of
*K*_{s}, based on soil samples analyzed in the laboratory, as well as
the parameters used for generating their ensembles. The saturated hydraulic
conductivities of sand and clay are perturbed independently of each other
with multiplicative perturbations sampled from a lognormal distribution.

The parameters of the van Genuchten retention curves *α*, *n*, and
*θ*_{r} are perturbed taking into account their mutual
correlation according to Carsel and Parrish (1988), who described their statistics
and transformed them into normally distributed variables via the Johnson
system (Johnson, 1970). Three main transformation functions
are available, i.e, the lognormal (LN), log-ratio (SB), and hyperbolic (SU):

where *V* denotes the parameter before transformation, bounded within the
range [*A* *B*], and *Y* denotes the transformed parameter with normal
distribution. In this work, the prior statistics of the van Genuchten
parameters are taken from the soil types “sandy loam” and “silt loam” in
Carsel and Parrish (1988), assumed as valid representations of our sand and clay,
respectively. In particular, the SB transformation has been used for all the
parameters, except for *n* of the sandy loam and *α* of the silt loam,
for which the LN transformation has been applied. The ensemble of transformed
parameters is generated by

where **y** is the vector containing transformed *α*, *n*, and
*θ*_{r}, **u** contains the transformed variable means,
**T** is an upper diagonal matrix, obtained from the Choleski
factorization of the covariance matrix of the three parameters (see
Table 2), and **z** is a vector of normal deviates
with mean equal to 0 and standard deviation *σ*_{VG}. The transformed
variables can be included in the matrix **X** when updating the
parameters, and can then be back-transformed in order to obtain the updated
values of the soil retention parameters.

The EnKF algorithm implemented here is actually an ensemble transform Kalman
filter (Bishop et al., 2001) that does not require the perturbation of
observations. On the other hand, the measurement error covariance matrix,
**R**, must be assumed to be known a priori. In this work,
**R** was estimated directly from the measurements, taking advantage
of the high time resolution of the collected data. Pressure head and water
content data were collected every 2 s and averaged every 10 min over a
40 s window to obtain the observations to assimilate. Over the same time
window, the data were linearly detrended and the residuals were used to
calculate the correlation coefficients between all pairs of observations. The
final covariance matrices were then assembled by multiplying the correlation
coefficients by the relevant standard deviations, assumed as 0.05 m and
0.025 for pressure head and water content, respectively. The subsurface
outflow measurements are assumed to be independent of the pressure head and
water content data, with a standard deviation equal to 8 % of the measured
discharge. All measurement error standard deviations have been estimated
based on the accuracy of the sensors and plausible positioning errors.

When assimilating multiple variables, proper normalization of the measurement
error covariance matrices, anomalies of the simulated data, and innovation
vectors were performed, using values of 0.6 m, 0.58, and
$\mathrm{4.17}\times {\mathrm{10}}^{-\mathrm{5}}$ m^{3} s^{−1} for pressure head, water content and subsurface
outflow, respectively. The normalization ensures that in multivariate
assimilation scenarios the covariance matrices in the Kalman gain are not
ill-conditioned (Camporese et al., 2009b; Evensen, 2003).

## 4.3 Data assimilation scenarios

A total of 17 data assimilation scenarios have been simulated, whereby the assimilation interval, the assimilated variables, the updated variables, and the uncertainty on the van Genuchten parameters were varied. Table 3 reports a summary of the main characteristics for each scenario. Assimilated variables may include water content only or with subsurface outflow, pressure head only or with subsurface outflow, and all three variables together. With regard to the updated variables, three cases have been analyzed: update of the state variables only; update of the state variables and saturated hydraulic conductivities for both sand and clay; update of the state variables, hydraulic conductivities and van Genuchten parameters, for both sand and clay. In all the data assimilation scenarios, observations were assimilated only during the first 5 days of simulation, leaving the final 7 days as a validation period, during which the ensemble was left to evolve freely. For comparison, two open loop simulations, i.e., without data assimilation, have also been carried out (Table 3).

^{1} OL1 and OL2 indicate open loop scenarios, i.e.,
simulations without data

assimilation.
^{2} WC, PH, and *Q* denote water content, pressure
head, and subsurface

outflow, respectively.
^{3} St. var., *K*_{s}, and V.G. indicate state variables
(in terms of

pressure head), saturated hydraulic conductivity, and
van Genuchten parameters,

respectively.

The performance of the simulations has been evaluated by means of the root mean square error (RMSE), computed for the different variables, i.e., pressure head, water content, and subsurface outflow. The root mean square error is calculated as

where *N*_{o} is the number of observations available (six, four, and
one for water content, pressure head, and subsurface outflow,
respectively), *S*_{i,j} refers to the simulated results of the *i*th
realization of the ensemble at the location of the *j*th observation
and *O*_{j} is the corresponding experimental value.
To obtain a meaningful comparison between the errors of different
variables, we also compute the time-averaged normalized root mean
square error, NRMSE,

where *N*_{T} is the number of time steps, *k* is the time index, and NF is
a normalization factor equal to 0.58, 0.60 m, and
$\mathrm{4.17}\times {\mathrm{10}}^{-\mathrm{5}}$ m^{3} s^{−1} (i.e., 2.5 L min^{−1}) for the water content, pressure
head, and subsurface discharge, respectively. The NRMSE is computed
separately for each variable and for the assimilation (*N*_{T}=120) and
validation (*N*_{T}=167) periods, but also as a global index of performance
averaged over all the variables and the two periods.

## 5.1 Preliminary simulations

A preliminary sensitivity analysis over a number of EnKF parameters has been
performed, in order to select a final and satisfactory setup for the
subsequent data assimilation scenarios. First, simulations with *N* equal to
32, 128 and 256 have been performed, and it has been found that an ensemble
size of 128 ensures a good tradeoff between performance and computational
effort. Some preliminary sensitivity analyses of the value of
*σ*_{VG} have also been performed, resulting in values of 0.1 and
0.25 for the scenarios with and without update of van Genuchten parameters,
respectively (Table 3).

Then, several dampening factor values (** β** in
Eqs. 7 and 13) were tested, including
combinations of different values for the update of system state and
parameters. Based on this analysis, a value of 1 has been chosen for the
update of the system state, whereas a dampening factor equal to 0.5 has
been selected for the update of the soil hydraulic parameters
(

*K*

_{s},

*α*,

*n*, and

*θ*

_{r}, for both sand and clay). This choice of dampening factors is consistent with previous studies (Brandhorst et al., 2017) and prevents abrupt changes in the retention curve parameters that could lead to difficulties in model convergence and hence loss of realizations.

According to these preliminary analyses, all scenarios reported in Table 3 have been simulated with an ensemble size of 128 and dampening factors of 1 and 0.5 for system state and parameters, respectively.

## 5.2 Overall EnKF performance

Table 4 and Fig. 4 summarize the
performance of the EnKF in all the data assimilation scenarios, expressed in
terms of NRMSE for the three measured variables (water content, WC, pressure
head, PH, and subsurface outflow, *Q*), and averaged separately over the
assimilation and validation windows. A comparison between scenarios 1–5 and
8–12 in Table 4, characterized by the same assimilated and
updated variables but different assimilation intervals, shows that
assimilating more frequently does not always result in significant
improvements of model predictions. The variable that benefits the most from
more frequent updates is subsurface outflow, especially in the scenarios
where *Q* is assimilated (e.g., compare scenarios 3–5 with 10–12).

Figure 4 highlights that most of the data assimilation
scenarios result in an improvement of model predictions for pressure head and
subsurface outflow, compared to the open loop simulations (data pairs below
the 45 ^{∘} reference line). However, in some scenarios, the filter
performance in predicting the water content is actually worse than in the
open loop. A close inspection of the values in Table 4
indicates that such scenarios are those where pressure head is assimilated,
alone or in conjunction with water content and subsurface outflow. This is
likely due to a combination of two factors: (i) only four out of six
tensiometers are available for assimilation, compared to the six WCR probes
available for water content, and (ii) the pressure head measurements are
characterized by relatively poor quality. This can be appreciated from the
pressure head data shown in Fig. 2, where diurnal disturbances
caused by temperature fluctuations (Warrick et al., 1998) are apparent.

## 5.3 Parameter estimation capabilities

To assess the capabilities and benefits of parameter estimation with the
EnKF, it is useful to compare scenarios with the same assimilated variables
but different updated variables. Figure 5a, c, and e show
the ratios between RMSE in data assimilation scenarios S6, S8, and S13 and
the corresponding open loop values for water content, pressure head, and
subsurface outflow, respectively. In these three scenarios, water content
alone is assimilated, but the updated variables are system state only in S6,
system state and saturated hydraulic conductivity in S8, and system state,
the *K*_{s} and van Genuchten parameters *α*, *n*, and
*θ*_{r} in S13. Figure 5a highlights that
progressively updating more parameters brings significant improvements in
water content prediction over the validation period, with reductions of the
NRMSE with respect to the open loop of almost 20 % when updating
*K*_{s} only and 60 % when also updating the retention curve
parameters. Moreover, updating parameters improves significantly pressure
head predictions in validation and subsurface outflow in both assimilation
and validation, as shown in Fig. 5c and e.

The effect of parameter updating on model predictions for scenarios S6, S8,
and S13 can be visualized in Fig. 6, which shows ensemble means
and 90 % confidence bands of simulated water content, pressure head, and
subsurface outflow in comparison with the experimental data and the
corresponding open loop values. In scenario S6, without parameter update,
model predictions during the validation tend to converge again to the open
loop simulations in terms of both mean and uncertainty
(Fig. 6a, d, g). Updating the parameters (scenarios S8 and S13)
results in decreased uncertainty during validation
(Fig. 6b, c, e, f, h, i), due to the reduced variability of
saturated hydraulic conductivity and van Genuchten parameters. Note also that
the update of *K*_{s} is particularly beneficial to pressure head
(panel a versus b and c, where it can be seen that, in the validation phase,
the ensemble mean with data assimilation departs the open loop and gets
closer to the measurements) and subsurface outflow (panel g versus h and i),
whereas updating *α*, *n*, and *θ*_{r} improved
significantly the water content (panel e versus f).

## 5.4 Tradeoffs in multi-source data assimilation

We now focus our attention on the scenarios where multi-source data are
assimilated. The right panels in Fig. 5 show the ratios
between RMSE in data assimilation scenarios S7, S10, and S15 and the
corresponding open loop values for water content, pressure head, and
subsurface outflow. Whereas in scenarios S6, S8, and S13 (see panels
**(a)**, **(c)** and **(e)** in Fig. 5)
water content alone was assimilated, in scenarios S7, S10, and S15 (see
panels **(b)**, **(d)** and **(f)** in
Fig. 5) water content and subsurface outflow were jointly
assimilated. The updated variables are system state only in S7, system state
and saturated hydraulic conductivity in S10, and system state plus
*K*_{s} and van Genuchten parameters *α*, *n*, and
*θ*_{r} in S15. As previously noted for the scenarios with
assimilation of water content alone, the effect of parameter updating is
significant mainly in the validation phase. However, one can now observe an
increase in validation RMSE of water content when also updating
*K*_{s}, with a value that exceeds the one of the corresponding open
loop. At the same time, there is a decrease in pressure head RMSE of more
than 40 % with respect to the open loop, indicating that the update of
*K*_{s} is beneficial to pressure head, but not to water content.
Including the update of van Genuchten parameters, in scenario S15, has an
opposite effect: model predictions of water content in validation improve
dramatically (RMSE of almost 60 % less than in the open loop), whereas
pressure head predictions worsen slightly and align with RMSE values of
scenario S13. This indicates that the update of the van Genuchten parameters
is more important for predictions of water content than pressure head, which
represents an interesting example of the kinds of tradeoffs associated with
multi-source data assimilation and parameter updating in integrated
hydrological models.

Further insights into the differences between scenarios S10 and S15 can be
gained from Figs. 7 and 8, which report the
prior and posterior (i.e., at the end of the assimilation period)
distributions of soil parameters. Fig. 7 reports the results for
scenario S10, where *K*_{s} only was updated, and shows that the sand
*K*_{s} is clearly identifiable, whereas the clay *K*_{s} is
not, with a large residual uncertainty and a mean value that is not
consistent with the actual soil type in the hillslope. As no data are
available in the clay layer, the large residual variability should be
expected, but the bias in the mean value is probably caused by spurious
correlations and, perhaps, also by the low sensitivity of the assimilated
variables to the clay permeability. This is likely the reason for the poor
model prediction of water content.

Figure 8 shows the prior and posterior distributions of
*K*_{s}, *α*, *n*, and *θ*_{r} in S15. Again, for the sand, the
saturated hydraulic conductivity can be clearly identified, as well as the
exponent *n* of the van Genuchten retention function, while parameters
*θ*_{r} and *α* are more difficult to estimate. As for the clay,
posterior uncertainty is large for all the parameters and the mean value of
*K*_{s} shows again a bias with respect to the prior value, although in this
case the final value is more consistent with the actual soil type and this
could explain why the water content model predictions improve significantly
compared to scenario S10. This can also be explained by the fact that all the
sensors are located in the sand layer, while no experimental data from the
clay layer are assimilated.

An additional perspective on parameter estimation is given by Fig. 9,
which shows the time evolution of ensemble mean and
spread of the saturated hydraulic conductivity and van Genuchten parameters
for both sand and clay in scenario S17 (one of the scenarios reported in
Fig. 10). The convergence toward stable values in the data
assimilation phase is only achieved for the parameters *K*_{s} and *n* of the
sand layer, while the dispersion remains generally higher for *θ*_{r} (to
which the model is typically not very sensitive) and *α*, as well as for
all the parameters of the clay layer.

In summary, the results of parameter updating for the clay show that data would be needed in all the soil layers. However, when dealing with large heterogeneous structures, it is very expensive to have every soil zone properly probed, which is why it is important to assess whether multivariate data assimilation approaches are capable of compensating for the lack of distributed observations with alternative sources of information. Here, an integrated measurement such as the subsurface outflow does not seem to be sufficient to compensate for this lack of representativeness.

Finally, we analyze the tradeoffs in system state predictions associated with multi-source data assimilation for scenarios S15, S16, and S17. Figure 10 shows pressure head in P2, water content in W6, and subsurface outflow as simulated in the data assimilation and open loop scenarios, in terms of ensemble mean and 90 % confidence bands, compared to the measurements. In scenario S15 (Fig. 10a, d, g), where water content and subsurface discharge were assimilated, model results are very good for these variables but not so for pressure head (see also NRMSE values in Table 4). On the other hand, in scenario S16, where pressure head and subsurface outflow were assimilated, pressure head and discharge are well simulated, but not water content (Fig. 10b, e, h, and Table 4). Finally, in scenario S17, where all the available data were assimilated, the model predicts well both pressure head and water content, but at the cost of a slightly degraded prediction of subsurface outflow compared to scenarios S15 and S16 (Fig. 10c, f, i, and Table 4).

Similar issues were reported by Zhang et al. (2016), who found that the joint assimilation of soil moisture and groundwater head does not improve model predictions, unless update localization is used. In their study, this was likely caused by unrealistic cross-variable correlations due to limited ensemble sizes, whereas in our case it might be that the relatively poor quality of pressure head measurements, compared to water content observations, and the lack of observations in the clay layer do not allow us to obtain accurate estimates of the van Genuchten parameters.

In this study, a Richards equation-based hydrological model, CATHY, has been used with the ensemble Kalman filter to assimilate pressure head, water content, and subsurface outflow data in a real-world test case, represented by an experimental artificial hillslope. A total of 17 data assimilation simulations have been presented and described to provide a comprehensive overview of possible scenarios. Univariate scenarios with the assimilation of water content or pressure head alone were compared to multivariate cases where water content and pressure head were combined with outflow discharge or where water content, pressure head and outflow discharge were jointly assimilated. Regarding the updating strategies, single (state variable) and joint (state variables plus saturated hydraulic conductivity with and without van Genuchten parameters) updating scenarios were considered.

Overall, the capabilities of the ensemble Kalman filter to jointly correct the system states and soil parameters in physically based hydrological models were confirmed, even in a real-world test case such as the one presented here, characterized by dominant unsaturated dynamics and hence strong nonlinearities. Updating of the saturated hydraulic conductivity brought significant improvements in the prediction of pressure head and subsurface outflow, while updating the van Genuchten parameters proved to be highly beneficial to the prediction of the water content dynamics. On the other hand, multivariate data assimilation may lead to significant tradeoffs. For instance, the assimilation of soil moisture in addition to pressure head and subsurface outflow improved water content, but slightly degraded the prediction of the outflow discharge. Moreover, our results suggest that high-quality and representative data are essential for a proper and effective use of data assimilation in physically based hydrological models, as shown by the relatively poor performance of the EnKF in scenarios when pressure head was assimilated, due to temperature disturbances of the data, and by biased estimates of clay parameters, due to the lack of data in this soil layer.

In future studies, more representative data, including observations in the clay, will be assimilated, and the possibility of applying bias-aware filters will be considered to compensate for the effect of temperature in the tensiometric data.

All the data are available from the corresponding author upon request.

AB and EB carried out the experiment. AB conducted the numerical simulations. AB and MC wrote the manuscript. MC supervised the research. All the authors reviewed the manuscript.

The authors declare that they have no conflict of interest.

We gratefully acknowledge the financial support of the University of Padua,
through grant CPDA148790. We thank the editor and three anonymous reviewers
for their detailed and very helpful comments.

Edited by: Harrie-Jan Hendricks Franssen

Reviewed by: three
anonymous referees

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