Modeling real-world phenomena, such as thermal, hydraulic, and mechanical (THM) interactions, involves the complex task of accurately representing systems while accounting for uncertainties in essential parameters. These uncertainties often stem from a range of data inaccuracies influenced by measurement limitations, environmental variability, and the inherent heterogeneity of samples, particularly in geologic contexts. Taking some examples from the figure on the side for instance, sensor accuracy, sample composition, conservation practices, and varying environmental conditions (e.g., temperature fluctuations) all contribute to the challenges of capturing reliable data. Addressing these factors is critical for creating models that can realistically reflect the behavior and interactions within natural systems, especially in fields reliant on precise simulation and forecasting.
The following examples demonstrate how variability/uncertainty in material properties affects model accuracy and reliability:
Shear strength is a critical parameter in geomechanical modelling that can be determined e.g. from cohesion (C) and angle of internal friction (phi). Sparse sampling (Diagram b-f. illustrating 5 data points for 5 artificial datasets, based on real measured data in Diagram a) for Oplalinus Clay with 17 data points) can have severe impact on the reliability of linear regression results with significant uncertainty in slope and intercept values (Diagram g).
Porosity can be measured with various technique e.g. dry sample or saturated sample measurements, nuclear magnetic resonance (NMR) measurement. These techniques differ not in the manner of sample preparation but even in the state the sample is during measurement (such as dry vs. saturated state) which can lead to significantly different measured values (see Figure on the right):
Additionally, sample composition also plays a major role on the data scatter: in the example presented here, carbonate presence in the middle region causes extreme posotiy values during the mearuement due to micro-shell inclusions. This further complicates statistical analysis and model integration as it often can lead to non-Gaussion distribution.
To assess the geological integrity of the host rock, that essentially acts as a barrier in the final disposal of nuclear waste, understanding and predicting the behavior of the repository over a long period of time is critical. Numerical investigations of barrier integrity involves assigning material properties to the host rock for THM simulations. If complete information were available, the material properties would be known functions of location, and features such as inhomogeneity and anisotropy could be expressed by spatially varying tensor-valued coefficients. In reality, however, information about variations in the structure and properties of the geological barrier is incomplete, which brings forth the questions:
A common approach to analyze the impact of heterogeneity is to model the rock mass as homogeneous in sections (e.g. geological layers), and in each of these sections, the considered material parameter values are modelled as random variables. This modelling approach yields fully correlated parameter description at two neighboring locations. A universal tool to describe randomness with a more general structure is the utilization of random fields whose realizations are functions of space that are generally not constants - e.g. Gaussian random field determined by its mean value and its two-point correlation function. In this representation, anisotropy can occur in two forms:
We present here a comparison study for both cases by choosing different correlation lengths for parallel and perpendicular directions for the first case and describing the dominant material property for each process in THM simulations as a tensor-valued random field for the second case: thermal conductivity for the thermal part, intrinsic permeability for the hydraulic part and elastic stiffness for the mechanical part. These properties play a key role in the evaluation of thermally induced excess pore water pressures and stress changes (Buchwald et. al., 2020; Chaudhry et. al., 2021).
To generate the random fields, we use the Karhunen-Loève expansion, which decomposes a random field into a series of orthogonal modes: the eigenfunctions capture the variability of the field at different spatial scales, while the associated eigenvalues quantify the proportion of variance carried by these eigenfunctions. The formula used to describe realizations for Gaussian random fields is given as:
$${Z(x,\xi) = Z_{mean}(x) + \sum^M_{i=1}(\xi_i \sqrt{\lambda_i} f_i(x)) }$$
where Zmean(x) is the mean of the field ξi ~ N(0,1), and fi and λi are eigenfunctions and eigenvalues of the covariance operator respectively, computed by solving the generalized eigenvalue problem numerically:
$${C f_i = \lambda_i M f_i}$$
$${ [C]_{i,j} = \int_D \phi_j(x) \int_D c(x,y) \phi_j(y) dy dx}$$
where φ is basis function, and c(x,y) is kernel/covariance function.
Solving the above problem for THM simulations brings in challenges:
We tackle these challenges by taking the following steps:
The case study used for the anisotropy and inhomogeneity impacts is a benchmark-type setup from previous cases (Chaudhry et al. 2021, Buchwald et al. 2020, Pitz et al. 2023): a circular 2D domain of 100m diameter with a circular hole in the center representing the emplaced high-radioactive waste cell (diameter of 2.48m).
We identify 3 input parameters with high degree of uncertainty: thermal conductivity (λ), intrinsic permeability (k) and Young’s modulus (E). To assess the impact of inhomogeneity and anisotropy, these three parameters are defined to represent said behavior. For clarity, we distinguish between material and statistical anisotropy:
A list of established scenarios is provided in the table below. In the first six homogeneous cases, spatially constant values were used for the three uncertain inputs. In the two cases labeled “Extreme”, all eight combinations of the three extreme values Ext ∈ {Min, Max} were simulated. In the cases labeled “Random,” the spatially constant values of the three inputs were randomly sampled from their probability distributions. The last four cases employed (spatially varying) random fields for the three input quantities.
As several cases were designed in this study to isolate the effects for both inhomogeneity and anisotropy, the detailes for each cases are discussed in parallel to emphasize the impacts. A brief summary of the most relevant results are listed below. For more details the reader is kindly referred to the article from Chaudhry et al. 2025.