Abstract
To enable proper remediation of accidental groundwater contamination, the contaminant plume evolution needs to be accurately estimated. In the estimation, uncertainties in both the contaminant source and hydrogeological structure should be considered, especially the temporal release history and hydraulic transmissivity. Although the release history can be estimated using geostatistical approaches, previous studies use the deterministic hydraulic property field. Geostatistical approaches can also effectively estimate an unknown heterogeneous transmissivity field via the use of joint data, such as a combination of hydraulic head and tracer data. However, tracer tests implemented over a contaminated area necessarily disturb the in situ condition of the contamination. Conversely, measurements of the transient concentration data over an area are possible and can preserve the conditions. Accordingly, this study develops a geostatistical method for the joint clarification of contaminant plume and transmissivity distributions using both head and contaminant concentration data. The applicability and effectiveness of the proposed method are demonstrated through two numerical experiments assuming a two-dimensional heterogeneous confined aquifer. The use of contaminant concentration data is key to accurate estimation of the transmissivity. The accuracy of the proposed method using both head and concentration data was verified achieving a high linear correlation coefficient of 0.97 between the true and estimated concentrations for both experiments, which was 0.67 or more than the results using only the head data. Furthermore, the uncertainty of the contaminant plume evolution was successfully evaluated by considering the uncertainties of both the initial plume and the transmissivity distributions, based on their conditional realizations.
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References
Adamson DT, Mahendra S, Walker KL Jr, Rauch SR, Sengupta S, Newell CJ (2014) A multisite survey to identify the scale of the 1,4-dioxane problem at contaminated groundwater sites. Environ Sci Technol Lett 1:254–258. https://doi.org/10.1021/ez500092u
Blackford LS, Choi J, Cleary A, D’Azevodo EF, Demmel J, Dhillon IS, Dongarra J, Hammarling S, Henry G, Petitet A, Stanley K, Walker DW, Whaley RC (1997) ScaLAPACK: a linear algebra library for message-passing computers. In: Proceedings of the eighth SIAM conference on parallel processing for scientific computing (PPSC 1997), Minnesota, USA, March 1997. Society for Industrial and Applied Mathematics
Box GEP, Cox DR (1964) An analysis of transformations. J R Stat Soc Ser B 26:353–360
Butera I, Tanda MG (2003) A geostatistical approach to recover the release history of groundwater pollutants. Water Resour Res 39(12):1372. https://doi.org/10.1029/2003WR002314
Cardiff M, Barrash W (2011) 3-D transient hydraulic tomography in unconfined aquifers with fast drainage response. Water Resour Res 47(12):W12518. https://doi.org/10.1029/2010WR010367
Cardiff M, Barrash W, Kitanidis PK, Malama B, Revil A, Straface S, Rizzo E (2009) A potential-based inversion of unconfined steady-state hydraulic tomography. Ground Water 47(2):259–270. https://doi.org/10.1111/j.1745-6584.2008.00541.x
Chen Z, Gomez-Hernandez JJ, Xu T, Zanini A (2018) Joint identification of contaminant source and aquifer geometry in a sandbox experiment with the restart ensemble Kalman filter. J Hydrol 564:1074–1084. https://doi.org/10.1016/j.jhydrol.2018.07.073
Chen Z, Xu T, Gomez-Hernandez JJ, Zanini A (2021) Contaminant spill in a sandbox with non-Gaussian conductivities: simultaneous identification by the restart normal-score ensemble Kalman filter. Math Geosci 53:1587–1615. https://doi.org/10.1007/s11004-021-09928-y
Cirpka OA, Kitanidis PK (2000) Sensitivity of temporal moments calculated by the adjoint-state method and joint inversing of head and tracer data. Adv Water Resour 24(1):89–103. https://doi.org/10.1016/S0309-1708(00)00007-5
De Sá VR, Koike K, Goto T, Nozaki T, Takaya Y, Yamasaki T (2021a) A combination of geostatistical methods and principal components analysis for detection of mineralized zones in seafloor hydrothermal systems. Nat Resour Res 30:2875–2887. https://doi.org/10.1007/s11053-020-09705-4
De Sá VR, Koike K, Goto T, Nozaki T, Takaya Y, Yamasaki T (2021b) 3D geostatistical modeling of metal contents and lithofacies for mineralization mechanism determination of a seafloor hydrothermal deposit in the middle Okinawa Trough, Izena Hole. Ore Geol Rev 135:104194. https://doi.org/10.1016/j.oregeorev.2021.104194
Deutsch CV, Journel AG (1998) GSLIB: geostatistical software library and user’s guide. Applied geostatistics series. Oxford University Press, New York
Ezzedine S, Rubin Y (1996) A geostatistical approach to the conditional estimation of spatially distributed solute concentration and notes on the use of tracer data in the inverse problem. Water Resour Res 32(4):853–861. https://doi.org/10.1029/95WR02285
Fienen MN, Clemo T, Kitanidis PK (2008) An interactive Bayesian geostatistical inverse protocol for hydraulic tomography. Water Resour Res 44(12):W00B01. https://doi.org/10.1029/2007WR006730
Fienen MN, Hunt R, Krabbenhoft D, Clemo T (2009) Obtaining parsimonious hydraulic conductivity fields using head and transport observations: a Bayesian geostatistical parameter estimation approach. Water Resour Res 45(8):W08405. https://doi.org/10.1029/2008WR007431
Gelhar LW, Welty C, Rehfeldt KR (1992) A critical review of data on field-scale dispersion in aquifers. Water Resour Res 28(7):1955–1974. https://doi.org/10.1029/92WR00607
Gyzl G, Zanini A, Fraczek R, Kura K (2014) Contaminant source and release history identification in groundwater: a multi-step approach. J Contam Hydrol 157:59–72. https://doi.org/10.1016/j.jconhyd.2013.11.006
Harvey CF, Gorelick SM (1995) Mapping hydraulic conductivity—sequential conditioning with measurements of solute arrival time, hydraulic-head, and local conductivity. Water Resour Res 31(7):1615–1626. https://doi.org/10.1029/95WR00547
Illuman WA, Liu X, Shinji T, Yeh TJ, Ando K, Saegusa H (2009) Hydraulic tomography in fractured granite: mizunami underground research site. Jpn Water Resour Res 45(1):W01406. https://doi.org/10.1029/2007WR006715
Jiang Y, Woodbury AD (2006) A full-Bayesian approach to the inverse problem for steady-state groundwater flow and heat transport. Geophys J Int 167:1501–1512. https://doi.org/10.1111/j.1365-246X.2006.03145.x
Kimura H, Muraoka S (1986) The 3D-SEEP computer code user’s manual. Japan Atomic Energy Research Institute, JAERI-M 86-091. https://doi.org/10.11484/jaeri-m-86-091
Kitanidis PK (1995) Quasi-linear geostatistical theory for inversing. Water Resour Res 31(10):2411–2419. https://doi.org/10.1029/95WR01945
Kitanidis PK, Lee J (2014) Principal component geostatistical approach for large-dimensional inverse problems. Water Resour Res 50(7):5428–5443. https://doi.org/10.1002/2013WR014630
Koike K, Kiriyama T, Lu L, Kubo T, Heriawan MN, Yamada R (2022) Incorporation of geological constraints and semivariogram scaling law into geostatistical modeling of metal contents in hydrothermal deposits for improved accuracy. J Geochem Explor 233:106901. https://doi.org/10.1016/j.gexplo.2021.106901
Lallemand-Barres P, Peaudecerf P (1978) Recherche des relations entre les valeurs de la dispersivite macroscopique d’un milieu aquifere, ses autres caracteristiques et les conditions de measures. Etude Bibliographique Bull BRGM III(4):277–284
Lee J, Kitanidis PK (2014) Large-scale hydraulic tomography and joint inversion of head and tracer data using the Principal Component Geostatistical Approach (PCGA). Water Resour Res 50(7):5410–5427. https://doi.org/10.1002/2014WR015483
Lee J, Yoon H, Kitanidis PK, Werth CJ, Valocchi AJ (2016) Scalable subsurface inverse modeling of huge data sets with an application to tracer concentration breakthrough data from magnetic resonance imaging. Water Resour Res 52(7):5213–5231. https://doi.org/10.1002/2015WR018483
Li W, Englert A, Cirpka OA, Vanderborght J, Vereecken H (2007) Two-dimensional characterization of hydraulic heterogeneity by multiple pumping tests. Water Resour Res 43(4):W04433. https://doi.org/10.1029/2006WR005333
Li W, Englert A, Cirpka OA, Vereecken H (2008) Three-dimensional geostatistical inversion of flowmeter and pumping test data. Ground Water 46(2):193–201. https://doi.org/10.1111/j.1745-6584.2007.00419.x
Luo N, Illuman WA, Zha Y (2022) Large-scale three-dimensional hydraulic tomography analyses of long-term municipal wellfield operations. J Hydrol 610:127911. https://doi.org/10.1016/j.jhydrol.2022.127911
Michalak AM (2008) A Gibbs sampler for inequality-constrained geostatistical interpolation and inverse modeling. Water Resour Res 44(9):1–14. https://doi.org/10.1029/2007WR006645
Michalak AM, Kitanidis PK (2002) Application of Bayesian inference methods to inverse modeling for contaminant source identification at Gloucester Landfill, Canada. Comput Methods Water Resour XIV(2):259–1266
Michalak AM, Kitanidis PK (2003) A method for enforcing parameter nonnegativity in Bayesian inverse problems with an application to contaminant source identification. Water Resour Res 39(2):1033. https://doi.org/10.1029/2002WR001480
Nowak W (2009) Best unbiased ensemble linearization and the quasi-linear Kalman ensemble generator. Water Resour Res 45(4):W04431. https://doi.org/10.1029/2008WR007328
OECD (2014) Nuclear site remediation and restoration during decommissioning of nuclear installations: a report by the NEA co-operative programme on decommissioning. Radioactive Waste Management, NEA No. 7192. https://doi.org/10.1787/9789264222182-en
Pickens JF, Grisak GE (1981) Scale-dependent dispersion in a stratified granular aquifer. Water Resour Res 17(4):1191–1211. https://doi.org/10.1029/WR017i004p01191
Pouladi B, Linde N, Longuevergne L, Bour O (2021) Individual and joint inversion of head and flux data by geostatistical hydraulic tomography. Adv Water Resour 154:103960. https://doi.org/10.1016/j.advwatres.2021.103960
Sanchez-Leon E, Leven C, Haslauer CP, Cirpka OA (2016) Combining 3D hydraulic tomography with tracer tests for improved transport characterization. Ground Water 54(4):498–507. https://doi.org/10.1111/gwat.12381
Shlomi S, Michalak AM (2007) A geostatistical framework for incorporating transport information in estimating the distribution of a groundwater contaminant plume. Water Resour Res 43(3):1–12. https://doi.org/10.1029/2006WR005121
Singh RM, Datta B (2004) Groundwater pollution source identification and simultaneous parameter estimation using pattern matching by artificial neural network. Environ Forensics 5(3):143–153. https://doi.org/10.1080/15275920490495873
Snodgrass MF, Kitanidis PK (1997) A geostatistical approach to contaminant source identification. Water Resour Res 33(4):537–546. https://doi.org/10.1029/96WR03753
Spitz K, Moreno J (1996) A practical guide to groundwater and solute transport modeling, 1st edn. Wiley, New York
Takai S, Shimada T, Takeda S, Koike K (2022) Evaluating the effectiveness of a geostatistical approach with groundwater flow modeling for three-dimensional estimation of a contaminant plume. J Contam Hydrol 251:104097. https://doi.org/10.1016/j.jconhyd.2022.104097
Troldborg M, Nowak W, Lange IV, Santos MC, Binning PJ, Bjerg PL (2012) Application of Bayesian geostatistics for evaluation of mass discharge uncertainty at contaminated sites. Water Resour Res 48(9):W09535. https://doi.org/10.1029/2011WR011785
Vu MT, Jardani A (2022) Mapping of hydraulic transmissivity field from inversion of tracer test data using convolutional neural networks. CNN-2T. J Hydrol 606:127443. https://doi.org/10.1016/j.jhydrol.2022.127443
Wagner BJ (1992) Simultaneous parameter estimation and contaminant source characterization for coupled groundwater flow and contaminant transport modelling. J Hydrol 135:275–303. https://doi.org/10.1016/0022-1694(92)90092-A
Wang X, Jardani A, Jourde H (2017) A hybrid inverse method for hydraulic tomography in fractured and karstic media. J Hydrol 551:29–46. https://doi.org/10.1016/j.jhydrol.2017.05.051
Wiedemeier TH, Rifai HS, Newell CJ, Wilson JT (1999) Natural attenuation of fuels and chlorinated solvents in the subsurface. Wiley, New York
Woodbury A, Sudicky E, Ulrych TJ, Ludwig R (1998) Three-dimensional plume source reconstruction using minimum relative entropy inversion. J Contam Hydrol 32:131–158. https://doi.org/10.1016/S0169-7722(97)00088-0
Xu M, Eckstein Y (1995) Use of weighted least-squares method in evaluation of the relationship between dispersivity and field scale. Ground Water 33(6):905–908. https://doi.org/10.1111/j.1745-6584.1995.tb00035.x
Xu T, Gomez-Hernandez JJ (2018) Simultaneous identification of a contaminant source and hydraulic conductivity via the restart normal-score ensemble Kalman filter. Adv Water Resour 112:106–123. https://doi.org/10.1016/j.advwatres.2017.12.011
Xu T, Gomez-Hernandez JJ, Chen Z, Lu C (2021) A comparison between ES-MDA and restart EnKF for the purpose of the simultaneous identification of a contaminant source and hydraulic conductivity. J Hydrol 595:125681. https://doi.org/10.1016/j.jhydrol.2020.125681
Zanini A, Kitanidis PK (2009) Geostatistical inversing for large-contrast transmissivity fields. Stochas Environ Res Risk Assess 23(5):565–577. https://doi.org/10.1007/s00477-008-0241-7
Zha Y, Yeh TCJ, Illman WA, Onoe H, Mok CMW, Wen JC, Huang SY, Wang W (2017) Incorporating geologic information into hydraulic tomography: a general framework based on geostatistical approach. Water Resour Res 53(4):2850–2876. https://doi.org/10.1002/2016WR019185
Zha Y, Yeh TCJ, Illman WA, Zeng W, Zhang Y, Sun F, Shi L (2018) A reduced-order successive linear estimator for geostatistical inversion and its application in hydraulic tomography. Water Resour Res 54(3):1616–1632. https://doi.org/10.1002/2017WR021884
Acknowledgements
This study was funded by the Secretariat of Nuclear Regulation Authority, Nuclear Regulation Authority, Japan. Sincere thanks are extended to the two anonymous reviewers for their essential and constructive comments and suggestions that improved the clarity of this manuscript.
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All authors contributed to the study conception and design. Data analysis and modeling were planned and performed by ST and KK. The first draft of the manuscript was written by ST, and all authors commented on previous versions of the manuscript. All authors read and approved the final manuscript.
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Appendix: Normalization of the Prior Model
Appendix: Normalization of the Prior Model
The geostatistical estimation of the transmissivity was implemented via the normalization of the prior model using the following procedure. More details are given in Kitanidis and Lee (2014).
List of symbols | ||
---|---|---|
Parameter | Dimension | |
All | ||
t | Time | |
x | Space | m × 1 |
mt | Number of unknowns (source intensity) | |
m | Number of unknowns (contaminant plume/transmissivity) | |
nz | Number of observations (concentration) | |
nφ | Number of observations (head) | |
δ(x) | Dirac delta function | |
Estimation of initial contaminant plume distribution | ||
s | Discretized unknown source intensity | mt × 1 |
z0 | Discretized unknown initial contaminant plume | m × 1 |
\({\varvec{z}}_{0}^{*}\) | Observation (initial concentration) | nz × 1 |
Hs,\({\varvec{H}}_{s}^{*}\) | Jacobian matrix (for whole domain/observations) | \(m \times m_{t} ,n_{z} \times m_{t}\) |
vz | Observation error | nz × 1 |
\(\sigma_{{R_{z} }}\) | Standard deviation of error | |
Rz | Error covariance matrix | nz × nz |
Xs | Known drift matrix | mt × ps |
βs | Unknown drift coefficients | ps × 1 |
Qs | Generalized prior covariance matrix of unknown function | mt × mt |
θs | Structure parameter of covariance Qs | |
\({\varvec{V}}_{{\hat{s}}}\) | Covariance matrix of estimated source intensity | mt × mt |
\({\varvec{V}}_{{\hat{z}}}\) | Covariance matrix of estimated initial contaminant plume | m × m |
Estimation of hydraulic transmissivity distribution | ||
n | Number of observations | |
r | Discretized unknown log-transmissivity | m × 1 |
z(t) | Discretized unknown contaminant plume at time t | m × 1 |
y | Observation | n × 1 |
\(\user2{\varphi }\) | Observation (head) | \(n_{\varphi } \times 1\) |
\({\varvec{z}}^{\user2{*}}\) | Observation (transient concentration) | \(n_{z} \times \left( {t_{0} , \ldots ,t_{end} } \right)\) |
\(\overline{\user2{t}}\) | Observation (mean travel time) | \(n_{z} \times 1\) |
H | Jacobian matrix | n × m |
v | Observation error | n × 1 |
\(\sigma_{R}\) | Standard deviation of error | |
R | Error covariance matrix | n × n |
X | Known drift matrix | m × p |
β | Unknown drift coefficients | p × 1 |
Q | Generalized prior covariance matrix of unknown function | m × m |
θr | Structure parameter of covariance Q | |
K | Rank of approximation of Q | |
\({\varvec{V}}_{{\hat{\user2{r}}}}\) | Covariance matrix of estimated transmissivity | m × m |
δr | Finite difference interval | |
εr | relative machine precision | |
\(\lambda_{i}\) | ith eigenvalue of Q | |
Vi | ith eigenvector of Q | m × 1 |
δls | Finite difference interval for line search | |
Conditional realization | ||
\(N_{{z_{0} }}\) | Number of realizations (initial contaminant plume) | |
Nr | Number of realizations (transmissivity) | |
\({\varvec{s}}_{{\varvec{u}}} , {\varvec{s}}_{{\varvec{c}}}\) | Unconditional/conditional realization of s | mt × 1 |
\({\varvec{z}}_{0_{{\varvec{c}}}}\) | Conditional realization of z0 | m × 1 |
\({\varvec{r}}_{{\varvec{u}}} , {\varvec{r}}_{{\varvec{c}}}\) | Unconditional/conditional realization of r | m × 1 |
Physical model | ||
u | Groundwater velocity | 2 × 1 |
T | Transmissivity | m × 1 |
Q f | Pumping rate | |
V | Actual groundwater velocity | 2 × 1 |
Rf | Retardation factor | |
λf | Decay constant | |
D | Dispersion tensor | 2 × 2 |
ε | Porosity | |
\(\alpha_{L} , \alpha_{T}\) | Dispersivity (longitudinal and transverse) | |
Dm | Molecular diffusion coefficient | |
τ | Tortuosity | |
Lp | Plume length |
First, the drift matrix X is replaced with its normalized and isomorphic matrix U such that
where \({\varvec{S}}_{X} \in {\mathbb{R}}^{p \times p}\) is a diagonal matrix of the singular values and the columns of \({\varvec{V}}_{X}^{{}} \in {\mathbb{R}}^{p \times p}\) are the orthonormal eigenvectors of \({\varvec{X}}^{T} {\varvec{X}}\). Then, U is used to compute the detrending matrix \({\varvec{P}} \in {\mathbb{R}}^{m \times m}\)
The next step is to detrend the low-rank covariance Q [Eq. (20)]. First, ZQ is replaced with \({\varvec{PZ}}_{Q}\). Then, the singular value decomposition of ZQ is calculated such that
where \({\varvec{U}}_{Z} \in {\mathbb{R}}^{m \times K}\) is the unitary matrix; \({\varvec{S}}_{Z} \in {\mathbb{R}}^{K \times K}\) is a diagonal matrix of the singular values; and the columns of \({\varvec{V}}_{Z}^{{}} \in {\mathbb{R}}^{K \times K}\) are the orthonormal eigenvectors of \({\varvec{Z}}_{Q}^{T} {\varvec{Z}}_{Q}\). Using \({\varvec{C}} = {\varvec{U}}_{Z}^{T} {\varvec{QU}}_{Z}\), Q is replaced with its detrended and isomorphic matrix PQP
Then, HQ and \({\varvec{HQH}}^{T}\) can be approximated as
Finally, \(\overline{\user2{r}}\) is updated iteratively by the following linear equation system corresponding to Eq. (6)
Once the optimal solution \(\hat{\user2{r}}\) is obtained, the posterior covariance \({\varvec {V}}_{{\hat{r}}}\) can be approximately calculated as
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Takai, S., Shimada, T., Takeda, S. et al. Joint Clarification of Contaminant Plume and Hydraulic Transmissivity via a Geostatistical Approach Using Hydraulic Head and Contaminant Concentration Data. Math Geosci 56, 333–360 (2024). https://doi.org/10.1007/s11004-023-10084-8
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DOI: https://doi.org/10.1007/s11004-023-10084-8